CN114031217A - Method for rapidly treating waste oil agent for carbon fiber spinning - Google Patents

Method for rapidly treating waste oil agent for carbon fiber spinning Download PDF

Info

Publication number
CN114031217A
CN114031217A CN202111404681.4A CN202111404681A CN114031217A CN 114031217 A CN114031217 A CN 114031217A CN 202111404681 A CN202111404681 A CN 202111404681A CN 114031217 A CN114031217 A CN 114031217A
Authority
CN
China
Prior art keywords
waste oil
oil agent
carbon fiber
solution obtained
fiber spinning
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
CN202111404681.4A
Other languages
Chinese (zh)
Inventor
张国良
陈秋飞
王磊
韩兴荣
杨平
林康
田甲由
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.)
Zhongfu Shenying Carbon Fiber Co Ltd
Original Assignee
Zhongfu Shenying Carbon Fiber 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 Zhongfu Shenying Carbon Fiber Co Ltd filed Critical Zhongfu Shenying Carbon Fiber Co Ltd
Priority to CN202111404681.4A priority Critical patent/CN114031217A/en
Publication of CN114031217A publication Critical patent/CN114031217A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/02Specific form of oxidant
    • C02F2305/026Fenton's reagent

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)

Abstract

The invention discloses a method for quickly treating waste oil agent for carbon fiber spinning, which comprises the following steps: heating the spinning waste oil agent in water bath at 50-75 ℃; FeSO4·7H2Dissolving O in the solution obtained in the step 1, and fully stirring; taking H with the mass fraction of 27%2O2Dropwise adding the solution obtained in the step (2) at the rate of 1 drop/second, after the continuous stirring reaction is finished, dropwise adding alkali liquor into the solution obtained in the step (3), adjusting the pH to 7-8, standing the solution obtained in the step (4) for 30-50min, and performing suction filtration to obtain a filtrate. The method treats the waste oil agent for spinning by a Fenton oxidation method which is simple to operate, and solves the key problems of high cost and low treatment efficiency of the waste oil agent in the carbon fiber production process.

Description

Method for rapidly treating waste oil agent for carbon fiber spinning
Technical Field
The invention belongs to the technical field of waste oil agent treatment, and particularly relates to a method for rapidly treating carbon fiber spinning waste oil agent.
Background
The oiling agent is an important auxiliary agent in the production process of the high-performance polyacrylonitrile carbon fiber, and the oiling agent can form a film on the surfaces of monofilaments uniformly, so that the monofilaments can be prevented from being adhered and doubled, and the fiber surfaces can be prevented from being rubbed and abraded in the production process, thereby effectively avoiding the defects on the fiber surfaces, and being an effective technical measure for improving the performances of the precursor and the carbon fiber. However, with continuous production and key process characteristics of carbon fiber materials, the production amount of waste oil agents is gradually increased, and certain pressure is brought to the ecological environment. The industrial process is mainly carried out by a professional waste disposal facility by adopting a high-temperature incineration method, and the method is expensive in treatment cost and is not environment-friendly.
Disclosure of Invention
The invention aims to provide a method for quickly and efficiently treating waste oil agent for spinning in the carbon fiber production process aiming at the defects and the defects of the prior art, and solves the key problems of high treatment cost and low efficiency of the waste oil agent in the carbon fiber industry.
In order to achieve the above purpose, the present invention can be realized by the following scheme:
a method for rapidly treating carbon fiber spinning waste oil agent comprises the following steps:
(1) weighing spinning waste oil into a container, stirring at low speed, and heating in water bath at 50-75 ℃;
(2) weighing FeSO4·7H2Dissolving O in the solution obtained in the step (1), and fully stirring;
(3) weighing 27% of H by mass fraction2O2Dropwise adding the mixture into the solution obtained in the step (2) at the speed of 1 drop/second, and continuously stirring;
(4) after the reaction is finished, dropwise adding alkali liquor into the solution obtained in the step (3), and adjusting the pH to 7-8;
(5) and (4) standing the solution obtained in the step (4) for 30-50min, and performing suction filtration to obtain a filtrate.
Further, FeSO4·7H2The amount of O is 0.001-0.01 a, H2O2The dosage is 0.05-0.2 a, wherein a is equal to the mass of the waste oil agent.
Compared with the prior art, the invention has the following advantages:
1. the cost is low, and the treatment efficiency is high;
2. the treatment process is quick, and the operation is simple;
3. is environment-friendly.
Detailed Description
The embodiment of the invention is used for quickly and efficiently treating the waste oil agent generated in the carbon fiber spinning process by a simple Fenton oxidation method, and the high-efficiency treatment of the waste oil agent can be realized by controlling the reaction temperature, the hydrogen peroxide dosage, the ferric salt dosage and other process conditions. The following provides a detailed description of specific embodiments of the present invention.
The method has strong applicability and high application value, and can be popularized and used in the post-treatment of the waste oil agent in the silicon oil agent industry.
Therefore, the method for treating the spinning waste oil agent by the Fenton oxidation method is an efficient and rapid treatment method, effectively reduces the Chemical Oxygen Demand (COD), reduces the treatment cost of the waste oil agent and protects the environment. The method can be applied to different fields relating to silicon oil agents.
Example 1
(1) Weighing 250g of spinning waste oil agent into a four-neck flask, stirring at a low speed, and heating in a water bath at 65 ℃;
(2) 0.75g of FeSO was weighed4·7H2Dissolving O in the solution obtained in the step (1), and fully stirring;
(3) 37.5g of 27% H are weighed out2O2Dropwise adding the solution obtained in the step (2) at the speed of 1 drop/second, and continuously stirring;
(4) after the reaction is finished, dropwise adding 30g/mL NaOH into the solution obtained in the step (3), and adjusting the pH value to 7;
(5) standing the solution obtained in the step (4) for 30-50min, and performing suction filtration to obtain a filtrate;
through detection, when the method is used for treating the waste oil agent, the COD removal rate reaches 89.5%, and the solution is clear and transparent after standing and settling for 2.1 hours.
Example 2
(1) Weighing 250g of spinning waste oil agent into a four-neck flask, stirring at low speed, and heating in water bath at 60 ℃;
(2) 0.75g of FeCl was weighed3·6H2Dissolving O in the solution obtained in the step (1), and fully stirring;
(3) 37.5g of 27% H are weighed out2O2Dropwise adding the mixture into the solution obtained in the step (2) at the speed of 1 drop/second, and continuously stirring;
(4) after the reaction is finished, dropwise adding 30g/mL NaOH into the solution obtained in the step (3), and adjusting the pH value to 7;
(5) standing the solution obtained in the step (4) for 30-50min, and performing suction filtration to obtain a filtrate;
through detection, the COD removal rate of the waste oil agent treated by the method reaches 72.1%, and the solution is yellow and transparent after standing and settling for 4 hours.
Example 3
(1) Weighing 250g of spinning waste oil agent into a four-neck flask, stirring at low speed, and heating in water bath at 55 ℃;
(2) 0.75g of FeSO was weighed4·7H2Dissolving O in the solution obtained in the step (1), and fully stirring;
(3) 18.75g of 27% H are weighed out2O2Dropwise adding the mixture into the solution obtained in the step (2) at the speed of 1 drop/second, and continuously stirring;
(4) after the reaction is finished, dropwise adding 30g/mL NaOH into the solution obtained in the step (3), and adjusting the pH value to 7;
(5) standing the solution obtained in the step (4) for 30-50min, and performing suction filtration to obtain a filtrate;
through detection, when the method is used for treating the waste oil agent, the COD removal rate reaches 85.2%, and the solution is clear and transparent after standing and settling for 5.4 hours.
Example 4
(1) Weighing 250g of spinning waste oil agent into a four-neck flask, stirring at low speed, and heating in water bath at 70 ℃;
(2) 1.5g of FeSO are weighed4·7H2Dissolving O in the solution obtained in the step (1), and fully stirring;
(3) 37.5g of 27% H are weighed out2O2Dropwise adding the mixture into the solution obtained in the step (2) at the speed of 1 drop/second, and continuously stirring;
(4) after the reaction is finished, dropwise adding 30g/mL NaOH into the solution obtained in the step (3), and adjusting the pH value to 7;
(5) standing the solution obtained in the step (4) for 30-50min, and performing suction filtration to obtain a filtrate;
through detection, when the method is used for treating the waste oil agent, the COD removal rate reaches 81.6%, and the solution is yellow and transparent after standing and settling for 4.6 hours.
Example 5
(1) Weighing 250g of spinning waste oil agent into a four-neck flask, stirring at low speed, and heating in water bath at 50 ℃;
(2) 0.38g of FeSO was weighed4·7H2Dissolving O in the solution obtained in the step (1), and fully stirring;
(3) 18.75g of 27% H are weighed out2O2Dropwise adding the mixture into the solution obtained in the step (2) at the speed of 1 drop/second, and continuously stirring;
(4) after the reaction is finished, dropwise adding 30g/mL NaOH into the solution obtained in the step (3), and adjusting the pH value to 7;
(5) standing the solution obtained in the step (4) for 30-50min, and performing suction filtration to obtain a filtrate;
through detection, when the method is used for treating the waste oil agent, the COD removal rate reaches 76.8%, and the solution is yellow and opaque after standing and settling for 6 hours.
Example 6
(1) Weighing 250g of spinning waste oil agent into a four-neck flask, stirring at a low speed, and heating in a water bath at 75 ℃;
(2) 1.5g of FeSO are weighed4·7H2Dissolving O in the solution obtained in the step (1), and fully stirring;
(3) 75g of 27% H are weighed out2O2Dropwise adding the mixture into the solution obtained in the step (2) at the speed of 1 drop/second, and continuously stirring;
(4) after the reaction is finished, dropwise adding 30g/mL NaOH into the solution obtained in the step (3), and adjusting the pH value to 7;
(5) standing the solution obtained in the step (4) for 30-50min, and performing suction filtration to obtain a filtrate;
through detection, when the method is used for treating the waste oil agent, the COD removal rate reaches 90.6%, and the solution is clear and transparent after standing and settling for 1.8 hours.
Example 7
(1) Weighing 250g of spinning waste oil agent into a four-neck flask, stirring at low speed, and heating in water bath at 60 ℃;
(2) 0.75g of FeSO was weighed4·7H2Dissolving O in the solution obtained in the step (1), and fully stirring;
(3) 75g of 27% H are weighed out2O2Dropwise adding the mixture into the solution obtained in the step (2) at the speed of 1 drop/second, and continuously stirring;
(4) after the reaction is finished, dropwise adding 30g/mL NaOH into the solution obtained in the step (3), and adjusting the pH value to 7;
(5) standing the solution obtained in the step (4) for 30-50min, and performing suction filtration to obtain a filtrate;
through detection, when the method is used for treating the waste oil agent, the COD removal rate reaches 78.4%, and the solution is clear and transparent after standing and settling for 3.5 hours.
The foregoing embodiments are merely illustrative of the present invention and are not limiting, and modifications, substitutions, and variations may be made thereto without departing from the spirit and scope of the invention.

Claims (8)

1. A method for rapidly treating waste oil agent for carbon fiber spinning is characterized by comprising the following steps:
(1) weighing spinning waste oil into a container, stirring at low speed, and heating at 50-75 ℃;
(2) weighing FeSO4·7H2Dissolving O in the solution obtained in the step (1), and fully stirring;
(3) weighing 27% of H by mass fraction2O2Dropwise adding the mixture into the solution obtained in the step (2), and continuously stirring;
(4) after the reaction is finished, dropwise adding alkali liquor into the solution obtained in the step (3), and adjusting the pH to 7-8;
(5) and (4) standing the solution obtained in the step (4), and performing suction filtration to obtain a filtrate.
2. The method for rapidly processing the waste oil agent for carbon fiber spinning according to claim 1, characterized in that: and (1) selecting a water bath heating mode for heating.
3. The method for rapidly processing the waste oil agent for carbon fiber spinning according to claim 1, characterized in that: in step (2), FeSO4·7H2The dosage of O is 0.001-0.01 a, wherein a is equal to the mass of the waste oil agent.
4. The method for rapidly processing the waste oil agent for carbon fiber spinning according to claim 1, characterized in that: in the step (3), the mass fraction of H is 27%2O2The dosage is 0.05-0.2 a, wherein a is equal to the mass of the waste oil agent.
5. The method for rapidly processing the waste oil agent for carbon fiber spinning according to claim 1, characterized in that: in the step (3), the dropping rate was 1 drop/sec.
6. The method for rapidly processing the waste oil agent for carbon fiber spinning according to claim 1, characterized in that: in the step (4), the alkali liquor is NaOH solution with the mass concentration of 30 g/mL.
7. The method for rapidly processing the waste oil agent for carbon fiber spinning according to claim 1, characterized in that: in the step (4), the standing time is 30-50 min.
8. The method for rapidly processing the waste oil agent for carbon fiber spinning according to claim 1, characterized in that: the container is a four-mouth flask.
CN202111404681.4A 2021-11-24 2021-11-24 Method for rapidly treating waste oil agent for carbon fiber spinning Pending CN114031217A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202111404681.4A CN114031217A (en) 2021-11-24 2021-11-24 Method for rapidly treating waste oil agent for carbon fiber spinning

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202111404681.4A CN114031217A (en) 2021-11-24 2021-11-24 Method for rapidly treating waste oil agent for carbon fiber spinning

Publications (1)

Publication Number Publication Date
CN114031217A true CN114031217A (en) 2022-02-11

Family

ID=80138667

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202111404681.4A Pending CN114031217A (en) 2021-11-24 2021-11-24 Method for rapidly treating waste oil agent for carbon fiber spinning

Country Status (1)

Country Link
CN (1) CN114031217A (en)

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006019321A1 (en) * 2004-08-20 2006-02-23 United Environmental Limited Improvements in and relating to waste treatment
CN102633322A (en) * 2012-04-17 2012-08-15 西安建筑科技大学 Semi-coke waste water pretreatment method based on Electro-Fenton oxidization technology
CN102923912A (en) * 2012-11-07 2013-02-13 浙江大学 Method for comprehensively treating sewage of chemical fiber oiling agents in production plants
CN103523958A (en) * 2013-10-13 2014-01-22 陕西盛迈石油有限公司 High-concentration spinning oil wastewater pretreatment system
CN106567140A (en) * 2016-10-27 2017-04-19 青岛大学 Refinement production method of refined kendir fiber
CN108264169A (en) * 2017-01-03 2018-07-10 黑龙江吉纳森生物工程股份有限公司 A kind of drilling well oil-containing waste water treating device

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006019321A1 (en) * 2004-08-20 2006-02-23 United Environmental Limited Improvements in and relating to waste treatment
CN102633322A (en) * 2012-04-17 2012-08-15 西安建筑科技大学 Semi-coke waste water pretreatment method based on Electro-Fenton oxidization technology
CN102923912A (en) * 2012-11-07 2013-02-13 浙江大学 Method for comprehensively treating sewage of chemical fiber oiling agents in production plants
CN103523958A (en) * 2013-10-13 2014-01-22 陕西盛迈石油有限公司 High-concentration spinning oil wastewater pretreatment system
CN106567140A (en) * 2016-10-27 2017-04-19 青岛大学 Refinement production method of refined kendir fiber
CN108264169A (en) * 2017-01-03 2018-07-10 黑龙江吉纳森生物工程股份有限公司 A kind of drilling well oil-containing waste water treating device

Non-Patent Citations (5)

* Cited by examiner, † Cited by third party
Title
唐建兴等: "短纤油剂废水降COD值研究", 《合成技术及应用》 *
孙海超等: "碳纤维原丝废油剂的不同处理工艺探讨", 《高科技纤维与应用》 *
张天骏: "纺丝油剂废水的处理工艺", 《科技资讯》 *
杨胜科等: "钻井废弃泥浆中CMC的协同降解方法研究", 《应用化工》 *
王翔等: "Fenton氧化预处理化纤纺丝油剂废水试验研究", 《广州化工》 *

Similar Documents

Publication Publication Date Title
CN103359878A (en) Treatment method for realizing zero emission of printing and dyeing wastewater
CN108545885B (en) Quality-based treatment and recycling integrated process for cone yarn printing and dyeing wastewater
US20230159361A1 (en) Anaerobic-ao-sacr combined advanced nitrogen removal system and technology for high ammonia-nitrogen wastewater
WO2015196731A1 (en) Method for treating reverse-osmosis concentrated water of printing and dyeing wastewater and recycling reverse-osmosis concentrated water for dyeing
CN104829049A (en) Reusing treatment method for printing and dyeing wastewater
CN108373240B (en) Quality-based treatment and recycling integrated process for cotton printing and dyeing wastewater
CN108360058A (en) A kind of electrolyte and stainless steel engraving method for etching stainless steel
CN110937762B (en) PVA-containing desizing printing and dyeing wastewater pretreatment method
CN114031217A (en) Method for rapidly treating waste oil agent for carbon fiber spinning
CN113651448A (en) Method for removing sulfate ions and chloride ions in wastewater by ultrahigh-lime-aluminum method
CN104926033A (en) Efficient treatment method for printing and dyeing wastewater
CN112337472A (en) Catalyst for removing COD (chemical oxygen demand) in wastewater by Fenton oxidation method, preparation method and application
CN107879555A (en) APMP pulping sewage integrated treatment process
DENG et al. Treatment of pharmaceutical wastewater containing recalcitrant compounds in a Fenton-coagulation process
CN101723541B (en) Advanced treatment method for wastewater produced by synthetic rubber
CN113003546B (en) Method for comprehensively utilizing high-COD waste sulfuric acid
CN100386475C (en) Water comprehensive utilization technology for cleaning electroplating nickel
CN105753204A (en) Method for treating textile biologically-dysoxidizable wastewater
CN112093882B (en) Method for pretreating binaphthol production wastewater
CN110642461B (en) Alkali-activated leather-immobilized bacillus pumilus/H2O2Method for purifying printing and dyeing wastewater
CN113716665A (en) Method for preparing flocculating agent by utilizing strong-acid wastewater containing phosphorus and sulfur
CN112759149A (en) Treatment method of high-concentration garlic slicing wastewater
CN109231540B (en) Method for decoloring and degrading dye wastewater by using alkali/solid oxidant system
CN115196798B (en) Method for promoting quick flocculation of chromium in water
CN110054352B (en) Method for removing calcium ions in garbage incineration power generation leachate by using ASBR (anaerobic sequencing batch reactor) process

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: 20220211

RJ01 Rejection of invention patent application after publication