CN107601804A - A kind of method that self-heating moulding oily sludge pyrolysis prepares adsorbent - Google Patents

A kind of method that self-heating moulding oily sludge pyrolysis prepares adsorbent Download PDF

Info

Publication number
CN107601804A
CN107601804A CN201710817060.6A CN201710817060A CN107601804A CN 107601804 A CN107601804 A CN 107601804A CN 201710817060 A CN201710817060 A CN 201710817060A CN 107601804 A CN107601804 A CN 107601804A
Authority
CN
China
Prior art keywords
adsorbent
destructive distillation
oily sludge
oil
mixed
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.)
Pending
Application number
CN201710817060.6A
Other languages
Chinese (zh)
Inventor
仝坤
滕济林
刘光全
张旭辉
许毓
吴鹏
孙静文
张璐超
张明栋
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.)
China National Petroleum Corp
Original Assignee
China National Petroleum Corp
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 China National Petroleum Corp filed Critical China National Petroleum Corp
Priority to CN201710817060.6A priority Critical patent/CN107601804A/en
Publication of CN107601804A publication Critical patent/CN107601804A/en
Pending legal-status Critical Current

Links

Classifications

    • 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 invention provides a kind of method that self-heating moulding oily sludge pyrolysis prepares adsorbent, this method includes:Aqueous oily sludge is mixed with destructive distillation residue, is molded, then carries out carbonization, the solid product completed after destructive distillation is adsorbent.Wherein, water contained oil sludge is mixed moisture control below 50% with destructive distillation residue, oil content is 6~10%, mix adhesive special simultaneously, enter roller briquetting machine after stirring to be molded, dry and moisture content is down to less than 4%, be re-fed into gas retort and be heated to 500~600 DEG C, caused fuel gas, which is returned to burn into gas retort, in retort process provides destructive distillation thermal source;Complete the product after destructive distillation to cool down with air heat-exchange, the material oil content after cooling is reduced to less than 0.3%, can be used as water process adsorbent, and adsorbance is up to more than the 70% of commercially available wooden adsorbent adsorbance;Hot-air is admitted to heating furnace and burnt with caused oil gas in retort process;Greasy filth prepares adsorbent and realizes recycling and innoxious.

Description

A kind of method that self-heating moulding oily sludge pyrolysis prepares adsorbent
Technical field
The present invention is on a kind of oil-containing fixed-end forces and application technology as the second resource, is on a kind of self-heating specifically The method that moulding oily sludge pyrolysis prepares adsorbent, and thus obtained adsorbent and its application.
Background technology
Pyrolysis is solid waste harmless treatment, the common technology of recycling, is widely used in house refuse, medical waste Deng treatment of wastes produced, and it is gradually available for the processing of oily sludge.The reduction of oily sludge pyrolysis processing can reach More than 50%, organic compound can be stablized, and caused liquid pyrolysis oil may be used as fuel and derivative chemical products etc.. In addition, the process of oily sludge is handled using pyrolysis way, the heavy metal accumulation in oily sludge can also be pyrolyzed In residue, and form of the heavy metal in pyrolysis residue is than having higher resistant to leaching in bottom ash after burning.It is residual after pyrolysis Slag may be used as pollutant sorbing material, or pyrolytic process provides energy and supported.
CN102874997A discloses a kind of oily sludge pyrolysis and its method of resource, wherein being into oily sludge Add colliery powder and Fe3O4Afterwards, mixture mixed successively, be granulated, preheating and drying (using pyrolysis gas as thermal source) and heat Solution, then the pyrolysis gas discharged with recirculated water to pre-dryer cool down, and the steam and hydro carbons in pyrolysis gas are respectively with containing greasy dirt Water and liquid hydrocarbon form condense out, and oil-polluted water enters sewage farm and does processing up to standard, and liquid hydrocarbon recycles, and body refuse is through work Rich magnetic carbonaceous adsorbent is made after change.
CN103553040A discloses a kind of oily sludge pyrolysis processing, wherein being hot altogether with oily sludge using petroleum coke Solution prepares porous carbon, including step:(1) oily sludge is carried out predrying;(2) oily sludge of gained is mixed with petroleum coke Uniformly;(3) oily sludge of well mixed gained and petroleum coke mixtures crushed, ground, screening;(4) by gained mixture Material is impregnated in compound activator solution, is dried after dipping;(5) obtained mixture is placed in pre-activate in low-temp reaction stove; (6) product of gained is placed in high temperature reaction stove and continues to activate, cool to normal temperature with the furnace;(7) gained activation products are added Washed to obtain solid product using distilled water after soaking in hydrochloric acid or sulfuric acid solution, solid product is dried to obtain porous carbon Material.
It is carbon containing using greasy filth and other height that above-mentioned greasy filth pyrolysis, which prepares porous carbon materials or the invention of carbonaceous adsorbent, Simultaneously prepared by activated processing for material copyrolysis, and relative cost is higher or complex process.This research is dry with itself using greasy filth It is quenched to evaporate product mixing, is not required to introduce external source carbon material, residue yield is few, and technique is relatively easy, processing cost is low, through moulding The generation of flying dust can be greatly decreased after processing, oil quality is good, and fume treatment difficulty reduces;The deep fat gas reuse reclaimed in processing Can partially or completely solve the demand of pyrolyzing heat.
The content of the invention
It is an object of the present invention to develop a kind of improved oil-containing fixed-end forces and recycling new technology, solve The problems such as thermic load present in existing oily sludge pyrolytic process is high, oil quality is poor, residue also needs harmless treatment, realize The minimizing of greasy filth, recycling and innoxious.
On the one hand, the invention provides a kind of oily sludge pyrolysis treating method, this method to include:
Aqueous oily sludge is mixed with its destructive distillation residue, is molded, then carries out carbonization.Complete consolidating after destructive distillation Body product can be used as adsorbent, and its adsorbance is close to traditional wood activated charcoal.That is, oily sludge pyrolysis processing of the invention Method, it is a kind of method that oily sludge pyrolysis processing prepares adsorbent.
According to specific embodiments of the present invention, oily sludge pyrolysis treating method of the invention, the destructive distillation residue contains Oil cut rate is less than 0.3%, and moisture content is less than 10%.Specifically, described destructive distillation residue can be that the dry distillation of oil mud of traditional handicraft is residual Slag or the solid residue (i.e. described adsorbent) prepared from greasy filth of the present invention pyrolysis.
According to specific embodiments of the present invention, oily sludge pyrolysis treating method of the invention, aqueous oily sludge In the mixed system mixed with destructive distillation residue, moisture content≤50%, oil content 6~10% are controlled.
According to specific embodiments of the present invention, oily sludge pyrolysis treating method of the invention, aqueous oily sludge In the mixed system mixed with destructive distillation residue, binding agent is also mixed with.Specifically, the main component of the binding agent is humic acid Sodium, it is according to 5~15 by humic acid, sodium hydroxide and water:0.5~2:What 50~200 ratio was mixed with, dosage For the 0.5%-2.0% of oily sludge amount.
According to specific embodiments of the present invention, oily sludge pyrolysis treating method of the invention, it was pyrolyzed to reduce Dust in journey, avoids pipeline blockage, and the mixture that aqueous oily sludge is mixed with destructive distillation residue first is sent into shaping system System shaping, prepares particle diameter in 10~50mm, and intensity and is dried to moisture content below 4%, then carry out in more than 30N particle Destructive distillation.
According to specific embodiments of the present invention, in oily sludge pyrolysis treating method of the invention, the bar of carbonization Part is:500-600 DEG C, 2~4h is pyrolyzed, seals anaerobic.
According to specific embodiments of the present invention, in oily sludge pyrolysis treating method of the invention, by retort process Caused fuel gas, which is used to burn, provides destructive distillation thermal source.
According to specific embodiments of the present invention, in oily sludge pyrolysis treating method of the invention, after completing destructive distillation Solid product cools down with air heat-exchange, and hot-air is sent into heating furnace and burnt with caused oil gas in retort process.
Pyrolysis residue of the invention by the use of itself is quenched, the petroleum resources of itself no longer needs extra fuel to realize as fuel It is pyrolyzed and prepares adsorbent, adsorbance exceedes wood activated charcoal.
The present invention method, can directly handle more homogeneous oily sludge include tank bottom mud, bottom of pond mud, the mud of refinery three, Oil-base mud and chemical engineering sludge etc., it can also be used to by sorting pretreatment, the ground sludge of centrifuging treatment and mixing greasy filth Deng.
On the other hand, present invention also offers a kind of adsorbent, it includes being pyrolyzed according to oily sludge of the present invention The solid product completed after destructive distillation that processing method obtains.Preferably, the adsorbent oil content is below 0.3%, specific surface area Reach 400-500m2/g。
On the other hand, the application present invention also offers described adsorbent in as water process adsorbent.More Body, the adsorbent can be used for Adsorption oily waste water COD, petroleum substance, its absorption property is up to commercially available wood More than the 70% of matter adsorbent adsorbance.
In summary, the invention provides a kind of self-heating moulding oily sludge pyrolysis to prepare adsorbent technique, wherein will contain (within 50%, oil content controls within the 10% moisture control) mixing according to a certain percentage of water greasy filth and destructive distillation residue, Shaping, pyrolysis can handle the aqueous larger greasy filth that conventional equipment can not be handled.The technique need not be carried out to oily sludge Dehydration pretreatment, as long as water contained oil sludge and destructive distillation residue are mixed according to a certain percentage, be molded, are pyrolyzed, significantly reduces Pretreatment cost, and by the way that the aqueous larger greasy filth that conventional equipment can not handle can be handled with powder forming technique.It is logical Cross adjustment pyrolysis parameters of rock (by the way that the pyrolysis temperature of greasy filth, extension or the mode such as pyrolysis time for shortening greasy filth is raised and lowered) simultaneously Activation is played by means of caused steam in greasy filth pyrolytic process, obtains the greasy filth residue with large specific surface area, can Used as adsorbent.Caused waste water is directly entered burner combustion with waste gas in pyrolytic process, and is discharged into flue gas Air, emit no waste water in whole production process.The technique is effectively by the use of caused lighter hydrocarbons after oil destructive distillation as thermal source, no External heat source is needed, reduces the wasting of resources, it is cost-effective.The present invention technology, can realize oily sludge harmless treatment and Recycling;Realize that the three wastes of discharge are up to standard;Adsorbent adsorbance prepared by greasy filth reaches wood activated charcoal adsorbance More than 70%, it is also used as the filtrate in water-treatment biological filter tank.
Brief description of the drawings
Fig. 1 is the schematic flow sheet that the self-heating moulding oily sludge pyrolysis of the present invention prepares the method for adsorbent.
Embodiment
The present invention will be further described with reference to embodiments, and these embodiments are not intended to limit the invention.
It is shown in Figure 1, should the invention provides a kind of method that self-heating moulding oily sludge pyrolysis prepares adsorbent Method mixes according to a certain percentage including water contained oil sludge with destructive distillation residue, control moisture content≤50%, oil content 6~10%, together When mix adhesive special, roller briquetting machine is entered after stirring and is molded, shaped article is using heat smoke drying to moisture content ≤ 4%, it is heated to 500~600 DEG C or so (can adjust temperature according to actual conditions) subsequently into gas retort, is produced in retort process Raw fuel gas foldback enters heating furnace burning and provides destructive distillation thermal source;Complete the product after destructive distillation to cool down with air heat-exchange, cooling Material oil content afterwards is reduced to less than 0.3%;Hot-air is admitted to heating furnace and burnt with caused oil gas in retort process.It is dry The dust concentration after bag-type dust of waste gas caused by dry section is less than 30mg/m3;According to the test to sulphur in greasy filth and residue, flue gas Middle SO2Content is in 100mg/m3Within, the technique greasy filth reclaimed water point and pyrolysis water are discharged into air with flue gas, entirely produce Emitted no waste water in journey.The technique effectively by the use of caused lighter hydrocarbons after oil destructive distillation as thermal source, is not required to extra fuel, reduced The wasting of resources, it is cost-effective, and bioxin will not be produced.
Embodiment 1
Adsorbent, greasy filth physico-chemical property such as table are prepared using scum bottom sludge caused by the condensed oil sewage treatment plant of Liaohe Oil Field 1:
The scum bottom sludge index of correlation of table 1
Moisture content, % Oil content, % Solid content, %
62.70 8.41 28.89
The weight proportion of scum bottom sludge and pyrolysis residue is 3:1, and 1.5% binding agent is added, after mixing is quenched, enter Roller briquetting machine is molded, balling-up intensity 35N/, and then shaped article enters the drying of indirect-heating rotary furnace and pyrolysis, pyrolysis temperature 550 DEG C, pyrolysis time 3h, you can obtain adsorbent product.
Adsorbent index such as table 2 prepared by scum bottom sludge:
Adsorbent index of correlation prepared by the scum bottom sludge of table 2
Under equal experiment condition, adsorbent prepared by scum bottom sludge is commercially available to oily waste water COD, petroleum-type removal ability The 120% of wooden adsorbent.
Embodiment 2
Adsorbent, greasy filth physico-chemical property such as table 3 are prepared using heavy oil greasy filth caused by the oil field of Xinjiang:
The heavy oil greasy filth index of correlation of table 3
Moisture content, % Oil content, % Solid content, %
57.97 12.04 29.99
The weight proportion of heavy oil greasy filth and pyrolysis residue is 4:1, and 1.0% binding agent is added, after mixing is quenched, enter Roller briquetting machine is molded, balling-up intensity 41N/, and then shaped article enters the drying of indirect-heating rotary furnace and pyrolysis, pyrolysis temperature 600 DEG C, pyrolysis time 3h, finally give adsorbent product.
Adsorbent index such as table 4 prepared by heavy oil greasy filth:
Adsorbent index of correlation prepared by the heavy oil greasy filth of table 4
Under equal experiment condition, adsorbent prepared by heavy oil greasy filth can reach to oily waste water COD, petroleum-type removal ability The 90% of commercially available wooden adsorbent.
Embodiment 3
Using the clay standby adsorbent of Xinjiang oil field oil product storage tank tank bottom, greasy filth physico-chemical property such as table 5:
The tank bottom mud index of correlation of table 5
Moisture content, % Oil content, % Solid content, %
25.12 43.06 31.82
The weight proportion of clear tank greasy filth and pyrolysis residue is 1:4, and 1.0% binding agent is added, after mixing is quenched, enter Roller briquetting machine is molded, balling-up intensity 32N/, and then shaped article enters the drying of indirect-heating rotary furnace and pyrolysis, pyrolysis temperature 550 DEG C, pyrolysis time 3h, finally give adsorbent product.
Adsorbent index such as table 6 prepared by tank bottom oil sludge:
Adsorbent index of correlation prepared by the tank bottom oil sludge of table 6
Under equal experiment condition, adsorbent prepared by tank bottom oil sludge can reach to oily waste water COD, petroleum-type removal ability The 75% of commercially available wooden adsorbent.
Embodiment 4
Adsorbent, greasy filth physico-chemical property such as table 7 are prepared using the greasy filth in Liaohe River oil field cleaning well site:
Table 7 is cleared out a gathering place greasy filth index of correlation
Moisture content, % Oil content, % Solid content, %
5.85 5.25 88.90
The greasy filth that will clear out a gathering place is crushed, and is stirred with 1.5% binding agent, is molded into roller briquetting machine, balling-up Intensity 43N/ is individual, and then shaped article enters the drying of indirect-heating rotary furnace and is pyrolyzed, 550 DEG C, pyrolysis time 3h of pyrolysis temperature, most Adsorbent product is obtained eventually.
Adsorbent index such as table 8 prepared by greasy filth of clearing out a gathering place:
Table 8 clear out a gathering place greasy filth preparation adsorbent index of correlation
Under equal experiment condition, adsorbent prepared by greasy filth of clearing out a gathering place can reach to oily waste water COD, petroleum-type removal ability The 80% of commercially available wooden adsorbent.
Embodiment 5
Adsorbent, greasy filth physico-chemical property such as table 9 are prepared using caused tank bottom oil sludge during Shengli Oil Field secondary oil recovery:
The tank bottom oil sludge index of correlation of table 9
Moisture content, % Oil content, % Solid content, %
76.30 18.00 5.70
The weight proportion of tank bottom oil sludge and pyrolysis residue is 2:1, content of binder 1.5%, after mixing is quenched, enter Roller briquetting machine is molded, balling-up intensity 38N/, and then shaped article enters the drying of indirect-heating rotary furnace and pyrolysis, pyrolysis temperature 600 DEG C, pyrolysis time 3h, finally give adsorbent product.
Adsorbent index such as table 10 prepared by tank bottom oil sludge:
Adsorbent index of correlation prepared by the tank bottom oil sludge of table 10
Under equal experiment condition, adsorbent prepared by tank bottom oil sludge can reach to oily waste water COD, petroleum-type removal ability The 90% of commercially available wooden adsorbent.
The present invention is only illustrated with the above-mentioned example that is embodied as, the structure and size of each part, pressure-resistant, set location and its company Connecing to be varied from.On the basis of technical solution of the present invention, all inventive principles according to the present invention are entered to individual part Capable improvement or equivalents, it should not exclude outside protection scope of the present invention.

Claims (11)

1. a kind of method that oily sludge pyrolysis prepares adsorbent, this method include:
Aqueous oily sludge is mixed with destructive distillation residue, the mixed system for controlling aqueous oily sludge to be mixed with destructive distillation residue In, moisture content≤50%, oil content 6~10%;
The mixed system that aqueous oily sludge is mixed with destructive distillation residue is sent into roller briquetting machine shaping, and dries to moisture content Less than 4%;
Dried material carries out carbonization, and the solid product completed after destructive distillation is adsorbent.
2. according to the method for claim 1, wherein, the destructive distillation residue oil content is less than 0.3%, and moisture content is less than 10%.
3. the method according to claim 11, wherein, in the mixed system that aqueous oily sludge mixes with destructive distillation residue, Also it is mixed with binding agent.
4. according to the method for claim 3, wherein, the main component of the binding agent is sodium humate, it is planted by corruption Acid, sodium hydroxide and water are according to 10:1:What 100 ratio was mixed with, dosage is the 0.5%-2.0% of greasy filth weight.
5. according to the method for claim 1, wherein, the oily sludge includes tank bottom mud, bottom of pond mud, the mud of refinery three, oil Base mud or chemical engineering sludge, or including by sorting pretreatment, the ground sludge mud of centrifuging treatment or mixing greasy filth Deng.
6. according to the method for claim 1, wherein, the condition of carbonization is:500~600 DEG C.
7. according to the method for claim 1, wherein, provide caused fuel gas in retort process to destructive distillation for burning Thermal source.
8. according to the method for claim 1, wherein, complete the solid product after destructive distillation and cooled down with air heat-exchange, hot-air Heating furnace is sent into burn with caused oil gas in retort process.
9. a kind of adsorbent, it includes the solid completed after destructive distillation obtained according to the method described in any one of claim 1~8 Product.
10. adsorbent according to claim 9, for the adsorbent oil content below 0.3%, specific surface area reaches 400- 500m2/g。
11. the adsorbent described in claim 9 or 10 is as water process adsorbent;Preferably, wherein being by the adsorbent For pollutants such as surfactant, petroleum-types in Adsorption oily waste water.
CN201710817060.6A 2017-09-12 2017-09-12 A kind of method that self-heating moulding oily sludge pyrolysis prepares adsorbent Pending CN107601804A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710817060.6A CN107601804A (en) 2017-09-12 2017-09-12 A kind of method that self-heating moulding oily sludge pyrolysis prepares adsorbent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710817060.6A CN107601804A (en) 2017-09-12 2017-09-12 A kind of method that self-heating moulding oily sludge pyrolysis prepares adsorbent

Publications (1)

Publication Number Publication Date
CN107601804A true CN107601804A (en) 2018-01-19

Family

ID=61063292

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710817060.6A Pending CN107601804A (en) 2017-09-12 2017-09-12 A kind of method that self-heating moulding oily sludge pyrolysis prepares adsorbent

Country Status (1)

Country Link
CN (1) CN107601804A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108913175A (en) * 2018-06-21 2018-11-30 中国矿业大学 A kind of combined cycle system and its application method based on abandoned biomass catalytic pyrolysis product processing organic wastewater
CN110540858A (en) * 2019-09-11 2019-12-06 山西领君重工机械设备有限公司 Oil sludge recovery treatment method
CN111233301A (en) * 2020-03-06 2020-06-05 山东产研绿洲环境产业技术研究院有限公司 Oil sludge treatment method and oil sludge treatment system
CN111621316A (en) * 2020-05-29 2020-09-04 浙江华环环境有限公司 Additive for recycling common industrial garbage and processing method
CN112479529A (en) * 2020-12-04 2021-03-12 湖北爱国环保技术开发有限公司 Process for treating oil sludge by dry distillation method
CN114671589A (en) * 2022-03-17 2022-06-28 中国科学院城市环境研究所 Method for synergistic harmless recycling treatment of oil sludge and fly ash

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102294217A (en) * 2011-06-23 2011-12-28 中国石油天然气集团公司 Method for preparing new oil-extraction wastewater adsorbent by using pyrolysis residues of oil sludge
CN102874997A (en) * 2011-07-11 2013-01-16 中国石油化工股份有限公司 Oil-containing sludge pyrolysis and its resource treatment method
CN103880007A (en) * 2014-04-16 2014-06-25 邹炎 Activated carbon or activated coke prepared from oily sludge and preparation device and method thereof
CN105273790A (en) * 2015-11-04 2016-01-27 雷春生 Oily sludge recycling harmless comprehensive utilization method
CN105749870A (en) * 2016-04-11 2016-07-13 长江大学 Sewage adsorbent based on oily dross and usage thereof
CN107098559A (en) * 2017-06-16 2017-08-29 南京塔川化工设备有限公司 A kind of oily sludge is from heat supply Non-oxygen pyrolytic equipment and its method for pyrolysis

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102294217A (en) * 2011-06-23 2011-12-28 中国石油天然气集团公司 Method for preparing new oil-extraction wastewater adsorbent by using pyrolysis residues of oil sludge
CN102874997A (en) * 2011-07-11 2013-01-16 中国石油化工股份有限公司 Oil-containing sludge pyrolysis and its resource treatment method
CN103880007A (en) * 2014-04-16 2014-06-25 邹炎 Activated carbon or activated coke prepared from oily sludge and preparation device and method thereof
CN105273790A (en) * 2015-11-04 2016-01-27 雷春生 Oily sludge recycling harmless comprehensive utilization method
CN105749870A (en) * 2016-04-11 2016-07-13 长江大学 Sewage adsorbent based on oily dross and usage thereof
CN107098559A (en) * 2017-06-16 2017-08-29 南京塔川化工设备有限公司 A kind of oily sludge is from heat supply Non-oxygen pyrolytic equipment and its method for pyrolysis

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108913175A (en) * 2018-06-21 2018-11-30 中国矿业大学 A kind of combined cycle system and its application method based on abandoned biomass catalytic pyrolysis product processing organic wastewater
CN108913175B (en) * 2018-06-21 2020-09-08 中国矿业大学 Combined cycle system for treating organic wastewater based on waste biomass catalytic pyrolysis products and use method thereof
CN110540858A (en) * 2019-09-11 2019-12-06 山西领君重工机械设备有限公司 Oil sludge recovery treatment method
CN111233301A (en) * 2020-03-06 2020-06-05 山东产研绿洲环境产业技术研究院有限公司 Oil sludge treatment method and oil sludge treatment system
CN111621316A (en) * 2020-05-29 2020-09-04 浙江华环环境有限公司 Additive for recycling common industrial garbage and processing method
CN112479529A (en) * 2020-12-04 2021-03-12 湖北爱国环保技术开发有限公司 Process for treating oil sludge by dry distillation method
CN112479529B (en) * 2020-12-04 2023-12-05 湖北爱国环保技术开发有限公司 Dry distillation process for treating oil sludge
CN114671589A (en) * 2022-03-17 2022-06-28 中国科学院城市环境研究所 Method for synergistic harmless recycling treatment of oil sludge and fly ash
CN114671589B (en) * 2022-03-17 2023-09-29 中国科学院城市环境研究所 Method for synergistic harmless recycling treatment of oil sludge and fly ash

Similar Documents

Publication Publication Date Title
CN107601804A (en) A kind of method that self-heating moulding oily sludge pyrolysis prepares adsorbent
Xue et al. Pyrolysis of sewage sludge by electromagnetic induction: Biochar properties and application in adsorption removal of Pb (II), Cd (II) from aqueous solution
Zhang et al. Biochar and hydrochar derived from freshwater sludge: Characterization and possible applications
Gong et al. Experimental study on catalytic pyrolysis of oil sludge under mild temperature
Liu et al. Characterization of human manure-derived biochar and energy-balance analysis of slow pyrolysis process
CN105038822B (en) The cleaning method and device of a kind of sludge
CN105906176B (en) A method of recycling, which is total to, using greasy filth and solid waste prepares light ceramic
CN105859105A (en) Sludge treatment and recycling method
CN105417918A (en) Technical method for treating civil sludge through microwave pyrolysis
CN1863606A (en) Thermolysis of organic waste in a ball furnace
CN101307244A (en) Oil-making method of double-bed interactive and circling type for pyrolyzing sludge
CN101113067A (en) Resource treating method for oil-containing sludge
CN107200455A (en) The processing method of oil-based drill cuttings and oily sludge
CN106277667A (en) A kind of reclaiming city domestic sludge utilizes technique
Liu et al. A review on control factors of pyrolysis technology for plants containing heavy metals
CN103663896A (en) Method and device for stabilizing heavy metal through pyrolysis of sludge
CN103008331A (en) Resource treatment method for household garbage and biochemical sludge
CN108238706B (en) System and process for step-by-step pyrolysis treatment of oily sludge
CN106694538B (en) System and method for targeted remediation of organic contaminated soil by sludge microwave gasification residues
CN108033657A (en) A kind of method for improving pyrolyzing sludge carbonization absorption property
RU75711U1 (en) TECHNOLOGICAL INSTALLATION DIAGRAM FOR THERMAL DISCONTINUATION OF INDUSTRIAL OIL-CONTAINING AND SOLID DOMESTIC WASTE
CN108585405A (en) A kind of thermoset carrier sludge supercharging self energizing pyrolysis installation and method
CN210176701U (en) System for municipal sludge deep reduction treatment
Yu et al. Pyrolysis/combustion potential and heavy metal risk of oily sludge and derived products in industrial scale
CN107572524A (en) A kind of method that activated carbon is prepared using sludge

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
RJ01 Rejection of invention patent application after publication

Application publication date: 20180119

RJ01 Rejection of invention patent application after publication