CN109500062B - Preparation method of waste tire resource material improved by excess sludge - Google Patents

Preparation method of waste tire resource material improved by excess sludge Download PDF

Info

Publication number
CN109500062B
CN109500062B CN201811527217.2A CN201811527217A CN109500062B CN 109500062 B CN109500062 B CN 109500062B CN 201811527217 A CN201811527217 A CN 201811527217A CN 109500062 B CN109500062 B CN 109500062B
Authority
CN
China
Prior art keywords
excess sludge
preparation
tire
waste tire
waste
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.)
Active
Application number
CN201811527217.2A
Other languages
Chinese (zh)
Other versions
CN109500062A (en
Inventor
陈英文
陈秀鹃
范梦婕
徐源
徐海涛
祝社民
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.)
Nanjing Jiekefeng Environmental Protection Technology Equipment Research Institute Co ltd
Nanjing Tech University
Original Assignee
Nanjing Jiekefeng Environmental Protection Technology Equipment Research Institute Co ltd
Nanjing Tech University
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 Nanjing Jiekefeng Environmental Protection Technology Equipment Research Institute Co ltd, Nanjing Tech University filed Critical Nanjing Jiekefeng Environmental Protection Technology Equipment Research Institute Co ltd
Priority to CN201811527217.2A priority Critical patent/CN109500062B/en
Publication of CN109500062A publication Critical patent/CN109500062A/en
Application granted granted Critical
Publication of CN109500062B publication Critical patent/CN109500062B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/40Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation

Landscapes

  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)
  • Carbon And Carbon Compounds (AREA)

Abstract

本发明涉及一种剩余污泥改良的废弃轮胎资源化材料的制备方法,由以下步骤得到:将废弃轮胎研磨成小颗粒,将废弃轮胎颗粒进行无氧高温热解形成热解炭;将热解炭通过清洗去除灰分、S等物质;将剩余污泥与热解炭进行超声混合;向混合物中添加粘结剂后继续进行超声混合;从混合物中取出粘附有剩余污泥的热解炭再次进行无氧高温热解,最终形成剩余污泥改良的废弃轮胎资源化材料。本发明制备的剩余污泥改良的废弃轮胎资源化材料,具有生物相容性优良、亲水性强等特点,可以用作生物挂膜载体、吸附材料、电极材料等,在工业生产中具有非常大的应用价值。

Figure 201811527217

The invention relates to a method for preparing waste tire recycling material improved by excess sludge. The carbon removes ash, S and other substances by cleaning; ultrasonically mixes excess sludge with pyrolytic carbon; adds binder to the mixture and continues ultrasonic mixing; removes the pyrolytic carbon with excess sludge from the mixture Anaerobic high-temperature pyrolysis is carried out to finally form waste tire recycling materials improved by excess sludge. The waste tire resource material improved by the excess sludge prepared by the invention has the characteristics of excellent biocompatibility, strong hydrophilicity, etc., can be used as a biological film carrier, adsorption material, electrode material, etc., and has very high performance in industrial production. great application value.

Figure 201811527217

Description

Preparation method of waste tire resource material improved by excess sludge
Technical Field
The invention relates to a preparation method of a waste tire resource material improved by excess sludge, belonging to the field of new materials.
Background
In recent years, the demand for various types of motor vehicles and transportation has increased dramatically, with a concomitant dramatic increase in the number of scrap tires. Most of the scrap tires are deposited in landfills, which has become one of the most potentially hazardous waste disposal problems. At present, the recycling of waste tires by pyrolysis technology has become a research hotspot. The pyrolytic carbon is a main product of waste tire pyrolysis, has high carbon content, but because of the limitation of raw materials, the pyrolytic carbon contains a large amount of ash, inorganic impurities and the like, reduces the surface polarity of the pyrolytic carbon, influences the biocompatibility of the pyrolytic carbon, and limits the application of the pyrolytic carbon in the fields of agriculture, biology, environment and the like. Therefore, how to improve the performance of the pyrolytic carbon and improve the application value of the pyrolytic carbon becomes an important link for recycling and comprehensively utilizing waste tire resources.
In addition to the waste disposal problem caused by waste tires, the rational disposal of excess sludge is an environmental problem that is urgently needed to be solved. At present, sludge treatment mainly depends on landfill, incineration and composting, and with the enhancement of environmental awareness, the traditional methods of landfill, land utilization, incineration and the like of sludge are increasingly limited, and if the sludge cannot be properly treated, more serious secondary pollution can be caused. Therefore, finding new sludge resource utilization technology is receiving more and more attention. The excess sludge contains a large amount of nutrient elements such as microorganisms, biological remains, organic matters, N, P and the like, so that the excess sludge is subjected to anaerobic carbonization to form the biomass charcoal, the treatment problem of the biomass charcoal can be effectively solved, the biomass charcoal is recycled, and secondary utilization is realized. The biomass charcoal with good biocompatibility is used as a multifunctional material and has wide application in the fields of agriculture, biology and environment.
Disclosure of Invention
The invention aims to provide a preparation method of a waste tire resource material with improved excess sludge for improving the defects of the prior art, which organically combines waste tire pyrolytic carbon and excess sludge biomass carbon on the basis of realizing waste resource and widens the application range of the waste tire pyrolytic carbon.
The technical scheme adopted by the invention is as follows: a preparation method of a waste tire resource material improved by excess sludge comprises the following specific steps:
(1) taking a certain amount of waste rubber tires, and grinding the waste rubber tires into small particles;
(2) carrying out oxygen-free high-temperature pyrolysis on the ground tire particles to form pyrolytic carbon;
(3) cleaning the pyrolytic carbon to remove substances such as ash, S and the like;
(4) taking a certain amount of excess sludge, and ultrasonically mixing the excess sludge and pyrolytic carbon to obtain a mixture;
(5) adding a binder into the mixture, and performing ultrasonic mixing again;
(6) and performing anaerobic high-temperature pyrolysis again to finally prepare the waste tire resource material with improved residual sludge.
Preferably, the particle size of the waste rubber tire particles is 1mm to 1 cm. Preferably, N is used as the gas for carrying out the oxygen-free high-temperature pyrolysis on the tire particles in the step (2)2Or inert gas such as Ar; the temperature range is 300-1000 ℃, and the pyrolysis time is 1-10 h.
Preferably, the ultrasonic frequency in the step (4) is 40-100Hz, and the mixing time is 1-10 h.
Preferably, the concentration of the excess sludge in the step (4) is 0.1g/L-10g/L, and the addition amount of the excess sludge is 1-10 times of the mass of the tire.
Preferably, the binder in step (5) is methyl cellulose, hydroxyethyl cellulose, hydroxymethyl cellulose, carboxymethyl cellulose, polyoxyethylene, polyvinyl alcohol, or the like.
Preferably, the concentration of the binder in the step (5) is 0.01g/L-1 g/L; the addition amount of the binder is 2-15 times of the mass of the tire.
Preferably, the ultrasonic frequency in the step (5) is 50-100Hz, and the mixing time is 1-24 h.
Preferably, the temperature range of the oxygen-free high-temperature pyrolysis in the step (6) is 400-.
Furthermore, the prepared waste tire resource material improved by the excess sludge has the application range of biological biofilm carrier, electrode material or adsorbing material and the like.
Has the advantages that:
the beneficial effects of the above technical scheme are that: based on the principle of 'waste improvement-making good for others' and the like, the waste tire pyrolytic carbon and the excess sludge biomass carbon are organically combined, the defect of the waste tire pyrolytic carbon is overcome by utilizing the good biocompatibility of the excess sludge biomass carbon, the problem of reasonable disposal of waste is solved, and the novel carbon-carbon composite material of the tire pyrolytic carbon-the excess sludge biomass carbon, which has the advantages of good biocompatibility, strong hydrophilicity and the like, is prepared, can be used as a biofilm carrier, an electrode material and an adsorbing material, and the application range of the waste tire pyrolytic carbon is widened.
Drawings
FIG. 1 is a flow chart of a waste tire recycling material improved by excess sludge according to the present invention.
Detailed Description
In order that the objects and advantages of the invention will be more clearly understood, the following description is given in conjunction with the accompanying examples. It is to be understood that the following text is merely illustrative of one or more specific embodiments of the invention and does not strictly limit the scope of the invention as specifically claimed.
Example 1
Taking 10g of waste rubber tires, crushing and grinding the waste rubber tires to form particles with the particle size of 1mm, wherein the tire particles are in the range of N2Pyrolyzing at 300 ℃ for 2h in an atmosphere to form pyrolytic carbon particles of waste tires, taking 100g of residual sludge with the concentration of 10g/L and the pyrolytic carbon particles to perform 40Hz ultrasonic mixing for 10h, adding 150g of methylcellulose with the concentration of 0.05g/L after mixing, and performing 50Hz ultrasonic mixing for 1 h. Then the pyrolytic carbon adhered with the excess sludge is added into N2And (3) pyrolyzing for 10h at 400 ℃ in the atmosphere to finally prepare the waste tire carbon material improved by the residual sludge. The prepared carbon material is used for biofilm formation, common waste tire pyrolytic carbon is used as a contrast, and the performance of the waste tire carbon material biofilm formation improved by the excess sludge is as shown in the following table.
Name of Material Film hanging time (d)
Pyrolytic carbon for common waste tire 40
Waste tire carbon material improved by residual sludge 25
Example 2
Taking 20g of waste rubber tires, crushing and grinding the waste rubber tires to form particles with the particle size of 0.5cm, wherein the tire particles are in the range of N2Pyrolyzing at 600 ℃ for 5h in an atmosphere to form pyrolytic carbon particles of waste tires, taking 100g of residual sludge with the concentration of 5g/L and the pyrolytic carbon particles to perform 70Hz ultrasonic mixing for 6h, adding 200g of hydroxyethyl cellulose with the concentration of 0.5g/L after mixing, and performing 95Hz ultrasonic mixing for 12 h. Then the pyrolytic carbon adhered with the excess sludge is added into N2Pyrolyzing for 7h at 700 ℃ in the atmosphere to finally prepare the waste tire carbon material improved by the residual sludge. The prepared carbon material is used as an electrode material, common waste tire pyrolytic carbon is used as a contrast, and the electrochemical properties of the waste tire carbon material improved by the excess sludge are shown in the following table.
Name of Material Cyclic voltammetric peak current (mA)
Pyrolytic carbon for common waste tire 1.6
Waste tire carbon material improved by residual sludge 3
Example 3
Taking 50g of waste rubber tires, crushing and grinding the waste rubber tires to form particles with the particle size of 1cm, placing the tire particles in Ar atmosphere,pyrolyzing for 10h at 1000 ℃ to form pyrolytic carbon particles of waste tires, taking 50g of residual sludge with the concentration of 0.1g/L and carrying out 100Hz ultrasonic mixing on the pyrolytic carbon particles for 2h, adding 100g of polyoxyethylene with the concentration of 1.0g/L after mixing, and carrying out 75Hz ultrasonic mixing for 24 h. Then the pyrolytic carbon adhered with the excess sludge is added into N2Pyrolyzing for 4h at 1000 ℃ in the atmosphere to finally prepare the waste tire carbon material improved by the residual sludge. The prepared carbon material is used for adsorbing materials, common waste tire pyrolytic carbon is used as a contrast, and phenol, phenanthrene and Cu are used2+The adsorption performance of the carbon material of the waste tire, which is used as the adsorption object and is modified by the residual sludge, is shown in the following table.
Waste tire carbon Material adsorption Performance Table with sludge modified under different conditions (adsorption Capacity ζ/(mg. g))
Figure BDA0001904755720000041

Claims (10)

1.一种剩余污泥改良的废弃轮胎资源化材料的制备方法,其具体步骤如下:1. A method for preparing a waste tire recycling material improved by excess sludge, the specific steps of which are as follows: (1)取一定量废弃橡胶轮胎,将其研磨成小颗粒;(1) Take a certain amount of waste rubber tires and grind them into small particles; (2)将研磨好的轮胎颗粒进行无氧高温热解形成热解炭;(2) The ground tire particles are subjected to anaerobic high temperature pyrolysis to form pyrolytic carbon; (3)将热解炭清洗;(3) Clean the pyrolytic carbon; (4)取一定量剩余污泥,将剩余污泥与热解炭进行超声混合得混合物;(4) Take a certain amount of excess sludge, and ultrasonically mix the excess sludge and pyrolysis carbon to obtain a mixture; (5)向混合物中添加粘结剂,再次进行超声混合;(5) Add a binder to the mixture, and perform ultrasonic mixing again; (6)再次进行无氧高温热解,最终制成剩余污泥改良的废弃轮胎资源化材料。(6) Carry out anaerobic high-temperature pyrolysis again, and finally make waste tire recycling material improved by excess sludge. 2.根据权利要求1所述的制备方法,其特征在于:废弃橡胶轮胎颗粒的粒径为1 mm-1cm。2 . The preparation method according to claim 1 , wherein the particle size of the waste rubber tire particles is 1 mm-1 cm. 3 . 3.根据权利要求1所述的制备方法,其特征在于:步骤(2)中轮胎颗粒进行无氧高温热解所用气体为N2或Ar;温度范围为300-1000 oC,热解时间为1-10 h。3. The preparation method according to claim 1, characterized in that: in step (2), the gas used for anaerobic high-temperature pyrolysis of tire particles is N 2 or Ar; the temperature range is 300-1000 ° C, and the pyrolysis time is 1-10 hours. 4.根据权利要求1所述的制备方法,其特征在于:步骤(4)中超声混合的频率为40-100Hz,超声混合的时间为1-10 h。4 . The preparation method according to claim 1 , wherein the frequency of ultrasonic mixing in step (4) is 40-100 Hz, and the time of ultrasonic mixing is 1-10 h. 5 . 5.根据权利要求1所述的制备方法,其特征在于:步骤(4)中剩余污泥的浓度为0.1 g/L-10 g/L,剩余污泥的添加量为轮胎质量的1-10倍。5 . The preparation method according to claim 1 , wherein the concentration of the excess sludge in step (4) is 0.1 g/L-10 g/L, and the addition amount of the excess sludge is 1-10 g/L of the tire mass. 6 . times. 6.根据权利要求1所述的制备方法,其特征在于:步骤(5)中所述的粘结剂为甲基纤维素、羟乙基纤维素、羟甲基纤维素、羧甲基纤维素、聚氧乙烯或聚乙烯醇。6 . The preparation method according to claim 1 , wherein the binder described in step (5) is methyl cellulose, hydroxyethyl cellulose, hydroxymethyl cellulose, and carboxymethyl cellulose. 7 . , polyoxyethylene or polyvinyl alcohol. 7.根据权利要求1所述的制备方法,其特征在于:步骤(5)中粘结剂的浓度为0.01 g/L-1 g/L;粘结剂的添加量为轮胎质量的2-15倍。7. The preparation method according to claim 1, characterized in that: in step (5), the concentration of the binder is 0.01 g/L-1 g/L; the addition amount of the binder is 2-15 g/L of the tire mass times. 8.根据权利要求1所述的制备方法,其特征在于:步骤(5)中的超声频率为50-100 Hz,混合时间为1-24 h。8 . The preparation method according to claim 1 , wherein the ultrasonic frequency in step (5) is 50-100 Hz, and the mixing time is 1-24 h. 9 . 9.根据权利要求1所述的制备方法,其特征在于:步骤(6)中无氧高温热解的温度范围为400-1000 oC,热解时间为2-10 h。9 . The preparation method according to claim 1 , wherein the temperature range of the oxygen-free high temperature pyrolysis in step (6) is 400-1000 ° C, and the pyrolysis time is 2-10 h. 10 . 10.根据权利要求1所述的制备方法,其特征在于:所制备出的剩余污泥改良的废弃轮胎资源化材料,应用范围有生物挂膜载体、电极材料或吸附材料。10 . The preparation method according to claim 1 , wherein the prepared waste tire recycling material improved by excess sludge can be used in biological film carrier, electrode material or adsorption material. 11 .
CN201811527217.2A 2018-12-13 2018-12-13 Preparation method of waste tire resource material improved by excess sludge Active CN109500062B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811527217.2A CN109500062B (en) 2018-12-13 2018-12-13 Preparation method of waste tire resource material improved by excess sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811527217.2A CN109500062B (en) 2018-12-13 2018-12-13 Preparation method of waste tire resource material improved by excess sludge

Publications (2)

Publication Number Publication Date
CN109500062A CN109500062A (en) 2019-03-22
CN109500062B true CN109500062B (en) 2021-04-20

Family

ID=65752581

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811527217.2A Active CN109500062B (en) 2018-12-13 2018-12-13 Preparation method of waste tire resource material improved by excess sludge

Country Status (1)

Country Link
CN (1) CN109500062B (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CA3148078C (en) * 2019-07-25 2024-01-02 Hyun Chang Lee Tire composition
CN111647907A (en) * 2020-05-21 2020-09-11 天津大学 Preparation method of self-supporting heteroatom-doped sludge carbon electrode material
CN114073932B (en) * 2020-08-14 2024-04-30 中国石油天然气集团有限公司 Oil adsorption material and preparation method thereof
CN116586402B (en) * 2023-04-24 2023-12-05 中城院(北京)环境科技股份有限公司 Decoration garbage treatment process adopting friction cleaning machine

Family Cites Families (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101012059A (en) * 2006-12-08 2007-08-08 清华大学 Method of manufacturing active carbon for waste water treatment using waste tyre
KR100793234B1 (en) * 2007-03-14 2008-01-10 주식회사 지피알 Waste Tire Sludge Extraction Device
KR100847511B1 (en) * 2007-05-17 2008-07-22 천명원 Solid fuels and preparation methods thereof
CN103666511B (en) * 2013-09-04 2015-09-02 北京神雾环境能源科技集团股份有限公司 Tire treatment system
CN104194420B (en) * 2014-09-24 2016-07-06 青岛理工大学 Method and device for producing low-ash carbon black by pyrolysis of waste tires
CN106566588A (en) * 2016-11-08 2017-04-19 湖南万容科技股份有限公司 Method for preparing forming fuel by utilizing sludge
CN107821090B (en) * 2017-12-27 2019-09-27 大连地拓环境科技有限公司 A kind of planting soil and preparation method thereof
CN107987866B (en) * 2018-01-15 2023-06-30 陕西科技大学 Device and method for efficiently depolymerizing solid waste by microwaves and co-producing bio-oil and biochar
CN108977250B (en) * 2018-08-31 2024-05-28 南京林业大学 Device and method for treating waste automobile tires and agricultural straw mixed fuel

Also Published As

Publication number Publication date
CN109500062A (en) 2019-03-22

Similar Documents

Publication Publication Date Title
CN109500062B (en) Preparation method of waste tire resource material improved by excess sludge
CN105776506B (en) A kind of Fe/C compound porous structure material and its preparation method and application
CN110127972B (en) A method for improving the efficiency of sludge anaerobic digestion while reducing the ecotoxicity of heavy metals
CN106076335B (en) A kind of preparation method and application of heterogeneous Fenton catalyst
WO2019218412A1 (en) Immobilized microbial agent for in situ remediation of contaminated sediments, preparation method and use
WO2016176906A1 (en) Method for producing canna indica biochar capable of adsorbing ammonia nitrogen and cadmium simultaneously
CN102553530B (en) Honeycomb-shaped microorganism carrier and preparation method thereof
CN104084128B (en) Changing food waste waste residue modification active sludge carbon is utilized for what waste water processed
CN111318254A (en) Preparation method of high-efficiency regenerated activated carbon
CN111204817B (en) Magnetic composite carbon prepared from harmful algal bloom and plastic and preparation method thereof
CN106390927B (en) Preparation method of biological carbon composite adsorption material for removing phosphate from surface water
CN112844385A (en) Biochar adsorption catalytic material capable of being recovered by magnetic force, preparation method and application
CN110340138A (en) Biochar enhanced microbial remediation method of Cr(VI)-cyanide composite polluted soil
CN108585391A (en) A kind of charcoal renovation agent of the marine sediment of heavy metal pollution and preparation method thereof and restorative procedure
CN107572524B (en) A kind of method that utilizes sludge to prepare activated carbon
CN109179410A (en) A kind of preparation method of biomass-based active carbon
CN111871371A (en) A kind of modified biochar adsorption material and preparation method and application thereof
JP2024542403A (en) Method for producing straw-derived biochar material with enhanced magnetic properties by red mud and method for using same
CN108905965A (en) The method that sludge bioleaching-pyrolysis Combined Treatment prepares heavy metal absorbent
CN111135792A (en) Multiwalled carbon nanotube hybrid sludge-based carbon composite material and preparation method and application thereof
CN106186249B (en) A kind of micro-nano iron sulfide/porous carbon composite material and its preparation and application of seaweed biomass
CN110922010A (en) Benthic microorganism ecological restoration agent for black and odorous water body sediment and preparation method thereof
CN104003386A (en) Method for preparing powder active carbon by taking cow dung as raw material
CN112495337B (en) Method for preparing ceramsite filter material by using oil-containing sludge
CN112062124A (en) Activated carbon prepared from domestic solid waste and preparation method and application thereof

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
GR01 Patent grant
GR01 Patent grant