CN108275859A - A kind of continuous greasy filth environment-friendly treating process - Google Patents

A kind of continuous greasy filth environment-friendly treating process Download PDF

Info

Publication number
CN108275859A
CN108275859A CN201810064280.0A CN201810064280A CN108275859A CN 108275859 A CN108275859 A CN 108275859A CN 201810064280 A CN201810064280 A CN 201810064280A CN 108275859 A CN108275859 A CN 108275859A
Authority
CN
China
Prior art keywords
greasy filth
pyrolysis
treating process
environment
continuous
Prior art date
Legal status (The legal status 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 status listed.)
Withdrawn
Application number
CN201810064280.0A
Other languages
Chinese (zh)
Inventor
刘潇洒
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Zhengzhou Yun Kai Industrial Equipment Technology Co Ltd
Original Assignee
Zhengzhou Yun Kai Industrial Equipment Technology Co Ltd
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 Zhengzhou Yun Kai Industrial Equipment Technology Co Ltd filed Critical Zhengzhou Yun Kai Industrial Equipment Technology Co Ltd
Priority to CN201810064280.0A priority Critical patent/CN108275859A/en
Publication of CN108275859A publication Critical patent/CN108275859A/en
Withdrawn legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/75Multi-step processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/77Liquid phase processes
    • B01D53/78Liquid phase processes with gas-liquid contact
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/06Treatment of sludge; Devices therefor by oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/10Treatment of sludge; Devices therefor by pyrolysis
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/121Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/06Sludge reduction, e.g. by lysis
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/40Valorisation of by-products of wastewater, sewage or sludge processing

Abstract

The present invention relates to oil-sludge treatment technical fields, disclose a kind of continuous greasy filth environment-friendly treating process.The continuous greasy filth environment-friendly treating process utilizes second-time burning method, twice combustion processing is carried out to pyrolysis waste residue and pyrolysis gas, prevent greasy filth that may be pyrolyzed incomplete problem in pyrolytic process, the pyrolysis not exclusively remaining chemical substance of institute is subjected to burning processing, environmental protection treatment is carried out to tail gas caused by greasy filth simultaneously, it prevents from subsequently discharging the pollution to environment, to substantially increase the using effect of the continuous greasy filth environment-friendly treating process.

Description

A kind of continuous greasy filth environment-friendly treating process
Technical field
The present invention relates to oil-sludge treatment technical field, specially a kind of continuous greasy filth environment-friendly treating process.
Background technology
Oily sludge refers to the sludge for being mixed into the mink cell focuses such as crude oil, various product oils, residual oil.Oily sludge is not nature It is inherently present, but has with crude oil, product oil since oilfield exploitation, petroleum refining process, transport, use, storage etc. are various Pass it is industrial, civilian, personal etc., caused by the reasons such as various accidents, misoperation, outmoded, the damaged, corrosion of equipment crude oil, at Product oil run, drip, leak, leak to ground, deposit to ocean, lake, river bed, mix and are formed with soil, water etc. Oil, Tu Heshui, or even the mixture of other pollutants such as it is blended with.Oily sludge is harmful, has to plant, aqueous bio Evil, skin, eyes and respiratory apparatus can be stimulated by evaporating aerial oil gas, and soil is made to lose the function of plant growth, processing It is difficult with repairing, it is one of the major pollutants of oil and petrochemical industry.
Chinese patent CN106746419A is related to a kind of oily sludge scale pyrolysis treatment systems, as shown in Figure 1, packet Charging Pre-sorting unit is included, is used for carrying out postsearch screening and separation of solid and liquid to oily sludge, desiccation pyrolysis unit is used for oil-containing Sludge carries out desiccation and pyrolytic reaction, dedusting condensing unit, be used for pyrolysis gas mixture caused by desiccation pyrolysis unit into Row dedusting and condensation, effluent processing unit, effluent processing unit receive the isolate of other units and are handled respectively. Can minimizing, stabilisation, innoxious, recycling finally be realized to the solids such as oily sludge or solid-liquid mixing class offal treatment It utilizes.
As Fig. 2, Chinese patent CN106957136 A provide a kind of processing method of oily sludge, oily sludge heated It stirs, is separated by solid-liquid separation after standing, obtains greasy filth and oily liq;Oily liq is passed through sewage disposal system and carries out grease The oil of separation is carried out purification by liquid extraction by separation;It is quenched that medicament progress is added into greasy filth, carries out deep dehydration again after quenched, obtains To dewatered greasy filth and filtrate, filtrate is carried out to the operation of water-oil separating again;Dewatered greasy filth is subjected to drying and other treatment, heat Solve charing process.Processing method of the present invention is simple and effective, realizes the minimizing of oily sludge, innoxious, recycling place Reason, and whole processing technology flow operations floor space is smaller, cost of investment is low.
When handling oily sludge, prior art flow is complicated, while being also difficult to carry out more oily sludge The processing of environmental protection.For this purpose, we have proposed a kind of continuous greasy filth environment-friendly treating process to solve the above problems.
Invention content
(One)The technical issues of solution
In view of the deficiencies of the prior art, the present invention provides a kind of continuous greasy filth environment-friendly treating process, have using second-time burning Method and the advantages of carry out environmental protection discharge to tail gas, solves complicated to oil-sludge treatment flow in the prior art and environmental-protecting performance Poor problem.
(Two)Technical solution
Above-mentioned using second-time burning method and to the purpose of the environmentally friendly discharge of tail gas progress to realize, the present invention provides following technical side Case:A kind of continuous greasy filth environment-friendly treating process, includes the following steps:
1)Oily sludge is recycled, the oily sludge recycled is placed into dehydrating tower, and it is de- to carry out machinery to oily sludge Water;2)By step 1)Oily sludge after middle carry out mechanical dehydration is placed into heating tower, and heated solvent is put into heating tower, Heated solvent is blended in heating tower with oily sludge and carries out heating work, until the moisture in completely out greasy filth;3)It will step Rapid 2)In greasy filth carry out greasy filth pyrolysis, greasy filth pyrolysis include first pyrolysis and second pyrolysis, first be pyrolyzed absolute pressure For hundred pas of 750-850, temperature is 100-150 DEG C, and the absolute pressure of the second pyrolysis is less than 4,500 pas, and temperature is 150-300 DEG C, is obtained To pyrolysis waste residue and pyrogenic steam;
4)Pyrolysis waste residue and pyrogenic steam are put into combustion chamber, carry out the burning processing of first time, and burning time is 10-30 points Clock;5)By step 4)In pyrolysis waste residue and pyrogenic steam cooling after ten minutes, carry out second-time burning in a combustion chamber, burn Time is 5-15 minutes;6)By step 5)In pyrolysis waste residue be sent into pyrolysis waste residue output device carry out after being cooled to 75 DEG C or less It sends out;
7)By step 5)In pyrogenic steam carry out cooling treatment, obtain cooling gas;
8)Cooling gas is fed through in reverse-flow alkali liquid washing tower, cooling gas is contacted using alkali wash water, gained Alkali cleaning tail gas is sent out from the top of reverse-flow alkali liquid washing tower, and gained alkali wash water is exported from the alkali wash water of reverse-flow alkali liquid washing tower It sends out;
9)The alkali cleaning tail gas of gained and acid solution, oxidant and ferrous ion are subjected to catalysis oxidation under the action of nickel-base catalyst Reaction;
10)By step 6)In pyrolysis waste residue filled, by step 9)In tail gas react it is up to standard after discharged.
Preferably, step 1)In oily sludge carried out the sampling of online composition and measured, calculate crude oil OL, water W, silt particle SR contents;Determine colloid JZ, the asphalitine LZ and paraffin SL ratios in the main ingredient that crude oil includes, it is described online at It includes being measured twice at the top and bottom of oily sludge that part sampling, which measures, its ratio is calculated according to precipitation status;Wherein OL+W+SR= 100%, OL=JZ+LZ+SL;Each component ratio note that top sampling in the wherein described online composition sampling measurement determines For:OL1, W1, SR1, JZ1, LZ1, SL1, each component ratio that bottom sampling determines are denoted as:OL2、W2、SR2、JZ2、 LZ2, SL2, the ratio after top and bottom measurement is comprehensive are estimated as:
OL=(OL1+OL2)/2,W=(W1+W2)/ 2, SR=(SR1+SR2)/2;
Preferably, the step 2)Greasy filth temperature after middle preheating is 250-400 DEG C.
Preferably, the step 2)In greasy filth the heated solvent in solid phase is isolated in extraction and separation tower, to heating Solvent is recycled, and is recycled in heating tower.
Preferably, step 2)In the sampling of heated solvent SO ratios and the composition measure in OL and W it is related, it is specific public Formula is as follows:SO=(kOL+pW)* V, wherein k are solvent parameters, and p is dilution parameters, and V is greasy filth volume;Consider the moisture content in greasy filth Dehydration can be preferably realized with the ratio of crude oil.
Preferably, the step 3)In the first pyrolysis time be 1-3 hour, the second pyrolysis time be 3-6 hours.
Preferably, the step 9)In oxidant be hydrogen peroxide.
Preferably, the step 9)In time of catalytic oxidation be 20-40 seconds, liquid air volume ratio is(5-15): 1, the temperature of the catalytic oxidation is 30-60 DEG C, and the acid solution is hydrochloric acid or oxalic acid, the oxidant and ferrous ion Molar ratio be 1:(2-8).
Preferably, the step 4)In first time ignition temperature be 300-500 DEG C.
Preferably, the step 5)In second of ignition temperature be 500-800 DEG C.
(Three)Advantageous effect
Compared with prior art, the present invention provides a kind of continuous greasy filth environment-friendly treating process, has following advantageous effect:
The continuous greasy filth environment-friendly treating process carries out twice combustion using second-time burning method to pyrolysis waste residue and pyrolysis gas Processing, and accurately control burning time, it is therefore prevented that greasy filth may be pyrolyzed incomplete problem in pyrolytic process, will be pyrolyzed Not exclusively the remaining chemical substance of institute carries out burning processing, while carrying out environmental protection treatment to tail gas caused by greasy filth, after preventing Pollution of the continuous discharge to environment is conducive to extensive to substantially increase the using effect of continuous greasy filth environment-friendly treating process Popularization.
Description of the drawings
Fig. 1 is a kind of oily sludge scale pyrolysis treatment systems schematic diagram;
Fig. 2 is a kind of processing method schematic diagram of oily sludge;
Fig. 3 is implementing procedure figure of the present invention.
Specific implementation mode
Below in conjunction with the embodiment of the present invention, technical solution in the embodiment of the present invention is clearly and completely retouched It states, it is clear that described embodiments are only a part of the embodiments of the present invention, instead of all the embodiments.Based on the present invention In embodiment, every other implementation obtained by those of ordinary skill in the art without making creative efforts Example, shall fall within the protection scope of the present invention.
Embodiment 1
A kind of continuous greasy filth environment-friendly treating process, as shown in figure 3, including the following steps:
1)Oily sludge is recycled, the oily sludge recycled is placed into dehydrating tower, and it is de- to carry out machinery to oily sludge Water;
2)By step 1)Oily sludge after middle carry out mechanical dehydration is placed into heating tower, and into heating tower, input heating is molten Agent, heated solvent are blended in heating tower with oily sludge and carry out heating work, until the moisture in completely out greasy filth, preheating Greasy filth temperature afterwards be 250-400 DEG C, greasy filth isolates the heated solvent in solid phase in extraction and separation tower, to heated solvent into Row recycling, recycles in heating tower;
3)By step 2)In greasy filth carry out greasy filth pyrolysis, greasy filth pyrolysis include first pyrolysis and second pyrolysis, first be pyrolyzed Absolute pressure be hundred pas of 750-850, temperature is 100-150 DEG C, and the absolute pressure of the second pyrolysis is less than 4,500 pas, and temperature is 150-300 DEG C, pyrolysis waste residue and pyrogenic steam are obtained, the first pyrolysis time is 1-3 hours, and the second pyrolysis time is that 3-6 is small When;
4)Pyrolysis waste residue and pyrogenic steam are put into combustion chamber, carry out the burning processing of first time, and burning time is 10-30 points Clock, first time ignition temperature are 300-500 DEG C;
5)By step 4)In pyrolysis waste residue and pyrogenic steam cooling after ten minutes, carry out second-time burning in a combustion chamber, fire It is 5-15 minutes to burn the time, and second of ignition temperature is 500-800 DEG C;
6)By step 5)In pyrolysis waste residue be sent into submittings after pyrolysis waste residue output device be cooled to 75 DEG C or less;
7)By step 5)In pyrogenic steam carry out cooling treatment, obtain cooling gas;
8)Cooling gas is fed through in reverse-flow alkali liquid washing tower, cooling gas is contacted using alkali wash water, gained Alkali cleaning tail gas is sent out from the top of reverse-flow alkali liquid washing tower, and gained alkali wash water is exported from the alkali wash water of reverse-flow alkali liquid washing tower It sends out;
9)The alkali cleaning tail gas of gained and acid solution, oxidant and ferrous ion are subjected to catalysis oxidation under the action of nickel-base catalyst Reaction, oxidant are hydrogen peroxide, and the time of catalytic oxidation is 20-40 seconds, and liquid air volume ratio is(5-15):1, catalysis oxidation The temperature of reaction is 30-60 DEG C, and acid solution be hydrochloric acid or oxalic acid, and the molar ratio of oxidant and ferrous ion is 1:(2-8);
10)By step 6)In pyrolysis waste residue filled, by step 9)In tail gas react it is up to standard after discharged.
Embodiment 2
A kind of continuous greasy filth environment-friendly treating process, includes the following steps:
1)Oily sludge is recycled, the oily sludge recycled is placed into dehydrating tower, and it is de- to carry out machinery to oily sludge Water;
2)By step 1)Oily sludge after middle carry out mechanical dehydration is placed into heating tower, and into heating tower, input heating is molten Agent, heated solvent are blended in heating tower with oily sludge and carry out heating work, until the moisture in completely out greasy filth;
3)By step 2)In greasy filth carry out greasy filth pyrolysis, greasy filth pyrolysis include first pyrolysis and second pyrolysis, first be pyrolyzed Absolute pressure be hundred pas of 750-850, temperature is 100-150 DEG C, and the absolute pressure of the second pyrolysis is less than 4,500 pas, and temperature is 150-300 DEG C, obtain pyrolysis waste residue and pyrogenic steam;
4)Pyrolysis waste residue and pyrogenic steam are put into combustion chamber, carry out the burning processing of first time;
5)By step 4)In pyrolysis waste residue and pyrogenic steam cooling after ten minutes, carry out second-time burning in a combustion chamber;
6)By step 5)In pyrolysis waste residue be sent into submittings after pyrolysis waste residue output device be cooled to 75 DEG C or less;
7)By step 5)In pyrogenic steam carry out cooling treatment, obtain cooling gas;
8)Cooling gas is fed through in reverse-flow alkali liquid washing tower, cooling gas is contacted using alkali wash water, gained Alkali cleaning tail gas is sent out from the top of reverse-flow alkali liquid washing tower, and gained alkali wash water is exported from the alkali wash water of reverse-flow alkali liquid washing tower It sends out;
9)The alkali cleaning tail gas of gained and acid solution, oxidant and ferrous ion are subjected to catalysis oxidation under the action of nickel-base catalyst Reaction;
10)By step 6)In pyrolysis waste residue filled, by step 9)In tail gas react it is up to standard after discharged.
Preferably, step 1)In oily sludge carried out the sampling of online composition and measured, calculate crude oil OL, water W, silt particle SR contents;Determine colloid JZ, the asphalitine LZ and paraffin SL ratios in the main ingredient that crude oil includes, it is described online at It includes being measured twice at the top and bottom of oily sludge that part sampling, which measures, its ratio is calculated according to precipitation status;Wherein OL+W+SR= 100%, OL=JZ+LZ+SL;Each component ratio note that top sampling in the wherein described online composition sampling measurement determines For:OL1, W1, SR1, JZ1, LZ1, SL1, each component ratio that bottom sampling determines are denoted as:OL2、W2、SR2、JZ2、 LZ2, SL2, the ratio after top and bottom measurement is comprehensive are estimated as:
OL=(OL1+OL2)/2,W=(W1+W2)/ 2, SR=(SR1+SR2)/2;
Preferably, the step 2)Greasy filth temperature after middle preheating is 250-400 DEG C.
Preferably, the step 2)In greasy filth the heated solvent in solid phase is isolated in extraction and separation tower, to heating Solvent is recycled, and is recycled in heating tower.
Preferably, step 2)In the sampling of heated solvent SO ratios and the composition measure in OL it is related, specific formula It is as follows:SO=(kOL+pW)* V, wherein k are solvent parameters, and p is dilution parameters, and V is greasy filth volume.
Preferably, the step 3)In the first pyrolysis time be 1-3 hour, the second pyrolysis time be 3-6 hours.
The step 4)In burning processing preferably when in heating tower air humidity be less than threshold value RH when stop burning, add Air humidity is measured using high temperature resistant hygrometer in thermal tower;
The step step 5)In burning processing preferably when harmful gas concentration be less than threshold value HG when stop burning;Harmful gas Bulk concentration is measured using SO2 or firedamp sensor;
Preferably, the step 9)In oxidant be hydrogen peroxide.
Preferably, the step 9)In time of catalytic oxidation be 20-40 seconds, liquid air volume ratio is(5-15): 1, the temperature of the catalytic oxidation is 30-60 DEG C, and the acid solution is hydrochloric acid or oxalic acid, the oxidant and ferrous ion Molar ratio be 1:(2-8).
Preferably, the step 10)In reaction it is up to standard refer to that the concentration that is measured using harmful gas sensor is less than can Discharge standard, the harmful gas sensor include the gas sensors such as CO, NO2, SO2, NH3, CH4.
Preferably, the step 4)In first time ignition temperature be 300-500 DEG C.
Preferably, the step 5)In second of ignition temperature be 500-800 DEG C.
Embodiment 3
A kind of continuous greasy filth environment-friendly treating process, includes the following steps:
1)Oily sludge is recycled, the oily sludge recycled is placed into dehydrating tower, and it is de- to carry out machinery to oily sludge Water;
2)By step 1)Oily sludge after middle carry out mechanical dehydration is placed into heating tower, and into heating tower, input heating is molten Agent, heated solvent are blended in heating tower with oily sludge and carry out heating work, until the moisture in completely out greasy filth;
3)By step 2)In greasy filth carry out greasy filth pyrolysis, greasy filth pyrolysis include first pyrolysis and second pyrolysis, first be pyrolyzed Absolute pressure be hundred pas of 750-850, temperature is 100-150 DEG C, and the absolute pressure of the second pyrolysis is less than 4,500 pas, and temperature is 150-300 DEG C, obtain pyrolysis waste residue and pyrogenic steam;
4)Pyrolysis waste residue and pyrogenic steam are put into combustion chamber, carry out the burning processing of first time;
5)By step 4)In pyrolysis waste residue and pyrogenic steam cooling after ten minutes, carry out second-time burning in a combustion chamber;
6)By step 5)In pyrolysis waste residue be sent into submittings after pyrolysis waste residue output device be cooled to 75 DEG C or less;
7)By step 5)In pyrogenic steam carry out cooling treatment, obtain cooling gas;
8)Cooling gas is fed through in reverse-flow alkali liquid washing tower, cooling gas is contacted using alkali wash water, gained Alkali cleaning tail gas is sent out from the top of reverse-flow alkali liquid washing tower, and gained alkali wash water is exported from the alkali wash water of reverse-flow alkali liquid washing tower It sends out;
9)The alkali cleaning tail gas of gained and acid solution, oxidant and ferrous ion are subjected to catalysis oxidation under the action of nickel-base catalyst Reaction;
10)By step 6)In pyrolysis waste residue filled, by step 9)In tail gas react it is up to standard after discharged.
Preferably, step 1)In oily sludge carried out the sampling of online composition and measured, calculate crude oil OL, water W, silt particle SR contents;Determine colloid JZ, the asphalitine LZ and paraffin SL ratios in the main ingredient that crude oil includes, it is described online at It includes being measured twice at the top and bottom of oily sludge that part sampling, which measures, its ratio is calculated according to precipitation status;Wherein OL+W+SR= 100%, OL=JZ+LZ+SL;Each component ratio note that top sampling in the wherein described online composition sampling measurement determines For:OL1, W1, SR1, JZ1, LZ1, SL1, each component ratio that bottom sampling determines are denoted as:OL2、W2、SR2、JZ2、 LZ2, SL2, the ratio after top and bottom measurement is comprehensive are estimated as:
OL=(OL1+OL2)/ 2, W=(W1+W2)/ 2, SR=(SR1+SR2)/2;
Preferably, the step 2)Greasy filth temperature after middle preheating is 250-400 DEG C.
Preferably, the step 2)In greasy filth the heated solvent in solid phase is isolated in extraction and separation tower, to heating Solvent is recycled, and is recycled in heating tower.
Preferably, step 2)In the sampling of heated solvent SO ratios and the composition measure in OL it is related, specific formula It is as follows:SO=(kOL+pW)* V, wherein k are solvent parameters, and p is dilution parameters, and V is greasy filth volume.
The step 5)In burning processing preferably when harmful gas concentration be less than threshold value HG when stop burning;Harmful gas Bulk concentration is measured using SO2 or firedamp sensor;
Preferably, the step 10)In reaction it is up to standard refer to that the concentration that is measured using harmful gas sensor is less than and can be discharged Standard, the harmful gas sensor include the gas sensors such as CO, NO2, SO2, NH3, CH4.
Preferably, above-mentioned to be used for step 5)With step 10)In each harmful gas sensor gathered data by data Acquisition module is sent after unifying gathered data to controller processing, and controller can also control mechanical dehydration, oil in each step The processes such as the online Determination of composition of mud, pyrolysis and burning realize the automatic operating of greasy filth environmental protection treatment, accurately control each step Implementation.
The beneficial effects of the invention are as follows:The continuous greasy filth environment-friendly treating process, using second-time burning method, to pyrolysis waste residue with And pyrolysis gas carries out twice combustion processing, it is therefore prevented that greasy filth may be pyrolyzed incomplete problem in pyrolytic process, will be hot The solution not exclusively remaining chemical substance of institute carries out burning processing, while carrying out environmental protection treatment to tail gas caused by greasy filth, prevents Pollution of the follow-up discharge to environment is conducive to big to substantially increase the using effect of the continuous greasy filth environment-friendly treating process The popularization of scale.
It although an embodiment of the present invention has been shown and described, for the ordinary skill in the art, can be with Understanding without departing from the principles and spirit of the present invention can carry out these embodiments a variety of variations, modification, replace And modification, the scope of the present invention is defined by the appended.

Claims (10)

1. a kind of continuous greasy filth environment-friendly treating process, which is characterized in that include the following steps:
1)Oily sludge is recycled, the oily sludge recycled is placed into dehydrating tower, and it is de- to carry out machinery to oily sludge Water;
2)By step 1)Oily sludge after middle carry out mechanical dehydration is placed into heating tower, and into heating tower, input heating is molten Agent, heated solvent are blended in heating tower with oily sludge and carry out heating work, until the moisture in completely out greasy filth;
3)By step 2)In greasy filth carry out greasy filth pyrolysis, greasy filth pyrolysis include first pyrolysis and second pyrolysis, first be pyrolyzed Absolute pressure be hundred pas of 750-850, temperature is 100-150 DEG C, and the absolute pressure of the second pyrolysis is less than 4,500 pas, and temperature is 150-300 DEG C, obtain pyrolysis waste residue and pyrogenic steam;
4)Pyrolysis waste residue and pyrogenic steam are put into combustion chamber, carry out the burning processing of first time, and burning time is 10-30 points Clock;
5)By step 4)In pyrolysis waste residue and pyrogenic steam cooling after ten minutes, carry out second-time burning in a combustion chamber, fire It is 5-15 minutes to burn the time;
6)By step 5)In pyrolysis waste residue be sent into submittings after pyrolysis waste residue output device be cooled to 75 DEG C or less;
7)By step 5)In pyrogenic steam carry out cooling treatment, obtain cooling gas;
8)Cooling gas is fed through in reverse-flow alkali liquid washing tower, cooling gas is contacted using alkali wash water, gained Alkali cleaning tail gas is sent out from the top of reverse-flow alkali liquid washing tower, and gained alkali wash water is exported from the alkali wash water of reverse-flow alkali liquid washing tower It sends out;
9)The alkali cleaning tail gas of gained and acid solution, oxidant and ferrous ion are subjected to catalysis oxidation under the action of nickel-base catalyst Reaction;
10)By step 6)In pyrolysis waste residue filled, by step 9)In tail gas react it is up to standard after discharged.
2. a kind of continuous greasy filth environment-friendly treating process according to claim 1, which is characterized in that the step 2)Middle preheating Greasy filth temperature afterwards is 250-400 DEG C.
3. a kind of continuous greasy filth environment-friendly treating process according to claim 1, which is characterized in that the step 2)In oil Mud isolates the heated solvent in solid phase in extraction and separation tower, is recycled to heated solvent, is recycled in heating tower It uses.
4. a kind of continuous greasy filth environment-friendly treating process according to claim 1, which is characterized in that the step 3)In first Pyrolysis time is 1-3 hours, and the second pyrolysis time is 3-6 hours.
5. a kind of continuous greasy filth environment-friendly treating process according to claim 1, which is characterized in that the step 9)In oxygen Agent is hydrogen peroxide.
6. a kind of continuous greasy filth environment-friendly treating process according to claim 1, which is characterized in that the step 9)In urge The time of oxidation is 20-40 seconds, and liquid air volume ratio is(5-15):1, the temperature of the catalytic oxidation is 30-60 DEG C, the acid solution is hydrochloric acid or oxalic acid, and the molar ratio of the oxidant and ferrous ion is 1:(2-8).
7. according to a kind of continuous greasy filth environment-friendly treating process of claim 1-6 any one of them, which is characterized in that the step 4)In first time ignition temperature be 300-500 DEG C.
8. according to a kind of continuous greasy filth environment-friendly treating process of claim 1-7 any one of them, which is characterized in that the step 5)In second of ignition temperature be 500-800 DEG C.
9. a kind of continuous greasy filth environment-friendly treating process according to claim 1, which is characterized in that the step 1)In contain Greasy dirt has carried out online composition sampling and has measured, and calculates crude oil OL, water W, silt particle SR contents;Determine the master that crude oil includes Colloid JZ, the asphalitine LZ in composition and paraffin SL ratios are wanted, it includes at the top of oily sludge that the online composition sampling, which measures, It is measured twice with bottom.
10. a kind of continuous greasy filth environment-friendly treating process according to claim 9, which is characterized in that the step 2)In Heated solvent SO ratios and the relationship of crude oil OL and moisture content W in composition sampling measurement are:SO=(kOL+pW)* V, Wherein k is solvent parameter, and p is dilution parameters, and V is greasy filth volume.
CN201810064280.0A 2018-01-23 2018-01-23 A kind of continuous greasy filth environment-friendly treating process Withdrawn CN108275859A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810064280.0A CN108275859A (en) 2018-01-23 2018-01-23 A kind of continuous greasy filth environment-friendly treating process

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810064280.0A CN108275859A (en) 2018-01-23 2018-01-23 A kind of continuous greasy filth environment-friendly treating process

Publications (1)

Publication Number Publication Date
CN108275859A true CN108275859A (en) 2018-07-13

Family

ID=62804692

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810064280.0A Withdrawn CN108275859A (en) 2018-01-23 2018-01-23 A kind of continuous greasy filth environment-friendly treating process

Country Status (1)

Country Link
CN (1) CN108275859A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109095743A (en) * 2018-08-24 2018-12-28 郑州高路亚环保科技有限公司 The overcritical organic stripping system of one kind and its technique
CN110054383A (en) * 2019-05-10 2019-07-26 马平 The pyrolysis processing method of oily sludge
CN110763719A (en) * 2019-11-14 2020-02-07 西南石油大学 Experimental device and method for thermal cracking of thickened oil into coke in-situ combustion process
CN111268884A (en) * 2020-03-31 2020-06-12 浙江科茂环境科技有限公司 Oil sludge treatment system and method
TWI765079B (en) * 2018-07-31 2022-05-21 張偉民 Method for treating crude oil tank bottom sludge
CN114751614A (en) * 2022-05-17 2022-07-15 大庆中林绿源生物环保有限公司 Technology for treating loose modified pyrolytic oil sludge

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
RU2151958C1 (en) * 1998-12-28 2000-06-27 Открытое акционерное общество "ВНИИЭТО" Method for thermal decontamination of solid wastes
CN1488591A (en) * 2002-10-10 2004-04-14 中国石油化工股份有限公司 Oil-containing sludge treating method
CN102658283A (en) * 2012-05-07 2012-09-12 浙江利保环境工程有限公司 New process for treating solid waste by taking thermal conditioning as secondary and pyrolysis as primary
CN103134053A (en) * 2011-11-22 2013-06-05 上海巴安水务股份有限公司 Drying incineration treatment method for sludge containing oil
CN106673388A (en) * 2016-12-28 2017-05-17 江苏碧诺环保科技有限公司 Oil sludge resourceful treatment process

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
RU2151958C1 (en) * 1998-12-28 2000-06-27 Открытое акционерное общество "ВНИИЭТО" Method for thermal decontamination of solid wastes
CN1488591A (en) * 2002-10-10 2004-04-14 中国石油化工股份有限公司 Oil-containing sludge treating method
CN103134053A (en) * 2011-11-22 2013-06-05 上海巴安水务股份有限公司 Drying incineration treatment method for sludge containing oil
CN102658283A (en) * 2012-05-07 2012-09-12 浙江利保环境工程有限公司 New process for treating solid waste by taking thermal conditioning as secondary and pyrolysis as primary
CN106673388A (en) * 2016-12-28 2017-05-17 江苏碧诺环保科技有限公司 Oil sludge resourceful treatment process

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI765079B (en) * 2018-07-31 2022-05-21 張偉民 Method for treating crude oil tank bottom sludge
CN109095743A (en) * 2018-08-24 2018-12-28 郑州高路亚环保科技有限公司 The overcritical organic stripping system of one kind and its technique
CN110054383A (en) * 2019-05-10 2019-07-26 马平 The pyrolysis processing method of oily sludge
CN110054383B (en) * 2019-05-10 2021-11-02 马平 Pyrolysis treatment method for oily sludge
CN110763719A (en) * 2019-11-14 2020-02-07 西南石油大学 Experimental device and method for thermal cracking of thickened oil into coke in-situ combustion process
CN111268884A (en) * 2020-03-31 2020-06-12 浙江科茂环境科技有限公司 Oil sludge treatment system and method
CN111268884B (en) * 2020-03-31 2024-04-09 浙江科茂环境科技有限公司 Oil sludge treatment system and method
CN114751614A (en) * 2022-05-17 2022-07-15 大庆中林绿源生物环保有限公司 Technology for treating loose modified pyrolytic oil sludge

Similar Documents

Publication Publication Date Title
CN108275859A (en) A kind of continuous greasy filth environment-friendly treating process
Xu et al. Treatment of urban sludge by hydrothermal carbonization
Huang et al. The migration and transformation behaviors of heavy metals during the hydrothermal treatment of sewage sludge
CA2743612C (en) Method and facility for treating waste drilling mud
CN102241998B (en) Treatment equipment and process of oily sludge and sand
US7935261B2 (en) Process for treating waste drilling mud
CN107200452B (en) Device and method for microwave pyrolysis of sludge
CN108558154A (en) The immediate processing method of oily sludge
CN108409077A (en) Oily sludge materialization coupled processing method
CN105174669A (en) Harmless treatment technology for waste oil base mud
WO2022067440A1 (en) Volatilization and oxidation of organic waste
Yu et al. Pyrolysis/combustion potential and heavy metal risk of oily sludge and derived products in industrial scale
CN208964859U (en) A kind of oil-gas field development oily waste harmless treatment device
CN105540933B (en) A kind of grease well acidizing returns discharge opeing immediate processing method and system
CN102010733B (en) Method and device for condensing and recovering shale oil in collecting tube section of oil shale retorting system
CN109022000A (en) A kind of oil-gas field development oil-containing fixed-end forces device
US20210032145A1 (en) Method and device for treating water-containing substance
CN201907980U (en) Alkaline sludge waste water treatment device
D’Urso et al. Closed Cycle Drying Process to Retrain Industrial Sludge into Construction Products
CN212293278U (en) Multi-stage treatment facility for oil sludge
CN105776814A (en) Integrated treatment system and method for dehydrating and drying oil-containing sludge
CA3026183C (en) Solidification of waste brine from in situ hydrocarbon recovery operations
CN205774016U (en) The complete processing system of oily sludge dehydration-mummification
Valdés et al. Experimental prediction of the agglomeration capability of waste vegetable oils (WVO) in relation to the recovery of coal from coal fines cleaning wastes (CFCW)
Khusnutdinov et al. Methods and technologies for the processing of water-hydrocarbon emulsions and technogenic raw materials of metallurgical and petrochemical enterprises: A review

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
WW01 Invention patent application withdrawn after publication

Application publication date: 20180713

WW01 Invention patent application withdrawn after publication