WO2024103672A1 - Method for enriching glass fibers in waste wind turbine blades - Google Patents

Method for enriching glass fibers in waste wind turbine blades Download PDF

Info

Publication number
WO2024103672A1
WO2024103672A1 PCT/CN2023/096219 CN2023096219W WO2024103672A1 WO 2024103672 A1 WO2024103672 A1 WO 2024103672A1 CN 2023096219 W CN2023096219 W CN 2023096219W WO 2024103672 A1 WO2024103672 A1 WO 2024103672A1
Authority
WO
WIPO (PCT)
Prior art keywords
mesh
particle size
wind turbine
turbine blades
oversize
Prior art date
Application number
PCT/CN2023/096219
Other languages
French (fr)
Chinese (zh)
Inventor
刘向辉
何发泉
Original Assignee
国能龙源环保有限公司
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 国能龙源环保有限公司 filed Critical 国能龙源环保有限公司
Publication of WO2024103672A1 publication Critical patent/WO2024103672A1/en

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29BPREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
    • B29B17/00Recovery of plastics or other constituents of waste material containing plastics
    • B29B17/04Disintegrating plastics, e.g. by milling
    • B29B17/0404Disintegrating plastics, e.g. by milling to powder
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29BPREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
    • B29B17/00Recovery of plastics or other constituents of waste material containing plastics
    • B29B17/02Separating plastics from other materials
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29BPREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
    • B29B17/00Recovery of plastics or other constituents of waste material containing plastics
    • B29B17/02Separating plastics from other materials
    • B29B2017/0213Specific separating techniques
    • B29B2017/0293Dissolving the materials in gases or liquids

Definitions

  • the invention relates to the field of recycling retired wind turbine blades, and in particular to a method for enriching glass fibers in discarded wind turbine blades.
  • Wind power generation is an important way for my country to develop low-carbon power. At present, the proportion of wind power generation in my country and even in the world is increasing year by year.
  • the main components of wind power generation are wind turbine blades, which account for a large proportion of the power generation cost.
  • the main material of wind turbine blades is a composite material formed by fiber and resin, and the fiber is mainly glass fiber.
  • the fiber is mainly glass fiber.
  • Early wind turbine blades were mainly made of glass fiber, and the mass proportion of glass fiber usually reached 60%, but there was a large amount of resin bonding, which was extremely unfavorable for the subsequent fiber utilization.
  • the complete resin and fiber separation process is costly and the process is long, making it difficult to fully apply.
  • the purpose of the present invention is to overcome the difficulty of glass fiber in existing waste wind turbine blades.
  • a method for collecting glass fibers from discarded wind turbine blades is provided. This method can greatly improve the applicable fields and application scope of the product by further enriching the fibers and increasing the glass fiber content of the product and appropriately reducing the resin content, thereby achieving the purpose of low-cost resource utilization.
  • the present invention provides a method for enriching glass fibers in waste wind turbine blades, the method comprising the following steps:
  • crushed materials (1) crushing the discarded wind turbine blades to obtain crushed materials, and controlling the proportion of particles with a particle size of more than 20 mesh in the crushed materials to be 10-30% by weight, and the proportion of particles with a particle size of 20-200 mesh to be ⁇ 20% by weight, and then screening and collecting the crushed materials with a particle size of 20-200 mesh;
  • the proportion of particles with a particle size of >20 mesh in the pulverized material is controlled to be 15-25% by weight.
  • the liquid-to-solid ratio of the water to the pulverized material with a particle size of 20-200 mesh is 20-60 mL/g.
  • the stirring temperature is 50-70°C.
  • the stirring time is 5-12 hours.
  • the liquid-to-solid ratio of the organic solvent to the sieve oversize A is 10-60 mL/g.
  • the liquid-to-solid ratio of the organic solvent to the sieve oversize A is 20-40 mL/g.
  • the organic solvent is selected from one or more of methanol, ethanol, ethylene glycol, polyethylene glycol, glycerol, methyl acetate and ethyl acetate.
  • the stirring temperature is 60-80°C.
  • the drying temperature is 80-105° C.
  • the drying time is 4-16 h.
  • the method of the present invention can make full use of the glass fibers in the waste wind turbine blades, enrich the glass fibers in the wind turbine blades by simple and quick means, and recover materials with high glass fiber enrichment by combining crushing and stirring, thereby facilitating their subsequent recycling.
  • the process has low energy consumption and is environmentally friendly.
  • the present invention provides a method for enriching glass fibers in waste wind turbine blades, the method comprising the following steps:
  • crushed materials (1) crushing the discarded wind turbine blades to obtain crushed materials, and controlling the proportion of particles with a particle size of more than 20 mesh in the crushed materials to be 10-30% by weight, and the proportion of particles with a particle size of 20-200 mesh to be ⁇ 20% by weight, and then screening and collecting the crushed materials with a particle size of 20-200 mesh;
  • the discarded wind turbine blades are blades that are retired from wind power plants or cannot be used due to accidents.
  • the blades are mainly composed of a thermosetting composite material composed of glass fibers (the content of other substances is extremely small and can be ignored, and the properties are not much different from the main components).
  • the glass fiber content in the discarded wind turbine blades is 50-85% by weight, and the resin content is 15-50% by weight.
  • step (1) it is necessary to simultaneously control the proportion of the pulverized material with a particle size of >20 mesh to be 10-30 weight % and the proportion of the particle size of 20-200 mesh to be ⁇ 20 weight %.
  • the proportion of the pulverized material with a particle size of >20 mesh is controlled to be 15-25% by weight.
  • the proportion of particle size >20 mesh in the material can be 15 weight %, 16 weight %, 17 weight %, 18 weight %, 19 weight %, 20 weight %, 21 weight %, 22 weight %, 23 weight %, 24 weight % or 25 weight %.
  • the liquid-to-solid ratio of the water to the pulverized material with a particle size of 20-200 mesh is 20-60 mL/g, preferably 30-60 mL/g, specifically 30 mL/g, 35 mL/g, 40 mL/g, 45 mL/g, 50 mL/g, 55 mL/g or 60 mL/g.
  • the stirring temperature is 50-70° C.
  • the stirring temperature can be 50° C., 55° C., 60° C., 65° C. or 70° C.
  • the stirring time is 5-12 hours.
  • the stirring time can be 5 hours, 6 hours, 7 hours, 8 hours, 9 hours, 10 hours, 11 hours or 12 hours.
  • the liquid-to-solid ratio of the organic solvent to the sieve material A is 10-60 mL/g, preferably 20-40 mL/g, specifically 20 mL/g, 25 mL/g, 30 mL/g, 35 mL/g or 40 mL/g.
  • the organic solvent is selected from one or more of methanol, ethanol, ethylene glycol, polyethylene glycol, glycerol, methyl acetate and ethyl acetate.
  • the stirring temperature is 60-80°C, and specifically can be 60°C, 65°C, 70°C, 75°C or 80°C.
  • the stirring time can be 2h, 3h, 4h, 5h, 6h, 7h or 8h.
  • step (3) of the present invention in order to avoid the subsequent organic components and crushed materials Therefore, in a preferred embodiment, after the stirring is completed, the mixture does not need to be cooled to room temperature, but is directly passed through an 80-mesh sieve immediately after the stirring is completed.
  • the liquid-to-solid ratio of the ethanol to the oversize material B can be 30 mL/g, 35 mL/g, 40 mL/g, 45 mL/g or 50 mL/g.
  • the stirring temperature can be 50°C, 55°C, 60°C, 65°C, 70°C, 75°C or 80°C
  • the stirring time can be 2h, 3h, 4h, 5h, 6h or 7h.
  • the drying temperature is 80-105°C, and the drying time is 4-16h.
  • the drying temperature can be 80°C, 85°C, 90°C, 95°C, 100°C or 105°C, and the drying time can be 4h, 7h, 10h, 13h or 16h.
  • the inventors obtained the above process conditions through a large number of experimental studies and full consideration of the differences in the degree of crushing of glass fibers and resins in the crushing stage, as well as the differences in the agglomeration of fibers and resins in the solution.
  • the method of the present invention can make full use of the glass fibers in the waste wind turbine blades, enrich the glass fibers in the wind turbine blades by simple and quick means, and recover materials with high glass fiber enrichment by combining overall crushing and stirring, which can facilitate their subsequent recycling.
  • the process has low energy consumption and is environmentally friendly.
  • This method can greatly improve the applicable fields and application scope of the product by further enriching the fiber, increasing the glass fiber content of the product, and appropriately reducing the resin content, thereby achieving the purpose of low-cost resource utilization.
  • the discarded wind turbine blades used in the following examples and comparative examples come from a domestic wind power plant, and the contents of glass fiber and resin are shown in Table 1.
  • oversize material B was mixed with ethanol at a liquid-to-solid ratio of ethanol to oversize material B of 40 mL/g, and then stirred at 60° C. for 5 h, followed by filtration, and the filtered solid was dried at 80° C. for 12 h.
  • oversize A (2) Mixing the oversize A with ethylene glycol (the liquid-to-solid ratio of ethylene glycol to oversize A is 30 mL/g), stirring at 70° C. for 4 h, and then immediately passing the mixture through an 80-mesh sieve while hot to obtain oversize B;
  • oversize material B was mixed with ethanol at a liquid-to-solid ratio of ethanol to oversize material B of 40 mL/g, and then stirred at 70° C. for 6 h, followed by filtration, and the filtered solid was dried at 80° C. for 10 h.
  • crushed materials (1) crushing the discarded wind turbine blades as a whole to obtain crushed materials, and controlling the proportion of particles with a particle size of more than 20 mesh to be 15.6% by weight, and the proportion of particles with a particle size of 20-200 mesh to be 36.76% by weight in the crushed materials, and then screening and collecting the crushed materials with a particle size of 20-200 mesh;
  • crushed materials (1) crushing the discarded wind turbine blades as a whole to obtain crushed materials, and controlling the proportion of particles with a particle size of more than 20 mesh to be 22.4% by weight, and the proportion of particles with a particle size of 20-200 mesh to be 34.33% by weight, and then screening and collecting the crushed materials with a particle size of 20-200 mesh;
  • oversize material B was mixed with ethanol at a liquid-to-solid ratio of ethanol to oversize material B of 40 mL/g, and then stirred at 70° C. for 5 h, followed by filtration, and the filtered solid was dried at 100° C. for 4 h.
  • step (1) the proportion of particles with a particle size of >20 mesh in the crushed material is controlled to be 2.48% by weight, and the proportion of particles with a particle size of 20-200 mesh is controlled to be 41.22% by weight, and then screening is performed to collect the crushed material with a particle size of 20-200 mesh.
  • step (1) the proportion of particles with a particle size of >20 mesh in the crushed material is controlled to be 43.86% by weight, and the proportion of particles with a particle size of 20-200 mesh is controlled to be 22.43% by weight, and then screening is performed to collect the crushed material with a particle size of 20-200 mesh.
  • the method for detecting the content of glass fiber is: accurately weigh the sample weight M1, and after calcining at 600°C for 3 hours, weigh the weight M2.

Landscapes

  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The present invention relates to the field of recovery of retired wind turbine blades, and discloses a method for enriching glass fibers in waste wind turbine blades. The method comprises: (1) crushing waste wind turbine blades to obtain a crushed material, then sieving same, and collecting the crushed material, which has a particle size of 20-200 mesh; (2) mixing the collected crushed material with a particle size of 20-200 mesh with water, then stirring same at 40-80°C for 2-16 h, and sieving same with a 140-mesh sieve to obtain an oversize product A; (3) mixing the oversize product A with an organic solvent, then stirring same at 40-80°C for 2-8 h, and sieving same with an 80-mesh sieve to obtain an oversize product B; and (4) mixing the oversize product B with ethyl alcohol, wherein the liquid-solid ratio of the ethyl alcohol to the oversize product B is 30-50 mL/g, then stirring same at 50-80°C for 2-7 h, filtering same, and drying a solid obtained by means of filtration at 60-150°C for 2-24 h. By means of the method of the present invention, glass fibers in waste wind turbine blades can be fully utilized; and as the glass fibers in the wind turbine blades are enriched via a simple and fast means, the subsequent recycling thereof is facilitated.

Description

一种富集废弃风电叶片中玻璃纤维的方法A method for enriching glass fibers in discarded wind turbine blades
相关申请的交叉引用CROSS-REFERENCE TO RELATED APPLICATIONS
本申请要求2022年11月14日提交的中国专利申请202211417649.4的权益,该申请的内容通过引用被合并于本文。This application claims the benefit of Chinese patent application 202211417649.4 filed on November 14, 2022, the contents of which are incorporated herein by reference.
技术领域Technical Field
本发明涉及退役风电叶片回收领域,具体涉及一种富集废弃风电叶片中玻璃纤维的方法。The invention relates to the field of recycling retired wind turbine blades, and in particular to a method for enriching glass fibers in discarded wind turbine blades.
背景技术Background technique
风力发电是我国低碳发展的重要途径,目前风力发电在我国甚至全球的发电比例逐年增加。风力发电过程的主要零部件是风电叶片,风电叶片在发电成本中占比较大。Wind power generation is an important way for my country to develop low-carbon power. At present, the proportion of wind power generation in my country and even in the world is increasing year by year. The main components of wind power generation are wind turbine blades, which account for a large proportion of the power generation cost.
目前风电叶片的主要材料为纤维与树脂形成的复合材料,纤维又以玻璃纤维为主。早期的风电叶片均以玻璃纤维为主,玻璃纤维质量占比通常可以达到60%,但是有大量树脂的胶合存在,对后续的纤维利用极为不利。与此同时,完全的树脂和纤维分离工艺成本较大,流程较长,很难完全应用。At present, the main material of wind turbine blades is a composite material formed by fiber and resin, and the fiber is mainly glass fiber. Early wind turbine blades were mainly made of glass fiber, and the mass proportion of glass fiber usually reached 60%, but there was a large amount of resin bonding, which was extremely unfavorable for the subsequent fiber utilization. At the same time, the complete resin and fiber separation process is costly and the process is long, making it difficult to fully apply.
发明内容Summary of the invention
本发明的目的是为了克服现有的废弃风电叶片中的玻璃纤维难 以分离的问题,提供一种收集废弃风电叶片中玻璃纤维的方法,本方法通过将纤维进一步富集,提高产品玻纤含量,适当降低树脂含量可以极大的提升产物的应有领域和使用范围,达到了低成本的资源化目的。The purpose of the present invention is to overcome the difficulty of glass fiber in existing waste wind turbine blades. In order to solve the separation problem, a method for collecting glass fibers from discarded wind turbine blades is provided. This method can greatly improve the applicable fields and application scope of the product by further enriching the fibers and increasing the glass fiber content of the product and appropriately reducing the resin content, thereby achieving the purpose of low-cost resource utilization.
为了实现上述目的,本发明提供一种富集废弃风电叶片中玻璃纤维的方法,所述方法包括以下步骤:In order to achieve the above object, the present invention provides a method for enriching glass fibers in waste wind turbine blades, the method comprising the following steps:
(1)将废弃风电叶片进行粉碎,得到粉碎物料,并控制粉碎物料中粒度>20目的占比为10-30重量%,粒度为20-200目的占比≥20重量%,然后进行筛分,并收集粒度为20-200目的粉碎物料;(1) crushing the discarded wind turbine blades to obtain crushed materials, and controlling the proportion of particles with a particle size of more than 20 mesh in the crushed materials to be 10-30% by weight, and the proportion of particles with a particle size of 20-200 mesh to be ≥20% by weight, and then screening and collecting the crushed materials with a particle size of 20-200 mesh;
(2)将收集得到的粒度为20-200目的粉碎物料与水混合,然后在40-80℃下搅拌2-16h,然后过140目筛,得到筛上物A;(2) mixing the collected pulverized material with a particle size of 20-200 mesh with water, stirring at 40-80° C. for 2-16 hours, and then passing through a 140-mesh sieve to obtain an oversize material A;
(3)将筛上物A与有机溶剂混合,然后在40-80℃下搅拌2-8h,然后过80目筛,得到筛上物B;(3) mixing the oversize A with an organic solvent, stirring at 40-80° C. for 2-8 hours, and then passing through an 80-mesh sieve to obtain an oversize B;
(4)将筛上物B与乙醇混合,所述乙醇与所述筛上物B的液固比为30-50mL/g,然后在50-80℃下搅拌2-7h,接着过滤,将过滤得到的固体在60-150℃下烘干2-24h。(4) Mix the sieve material B with ethanol, wherein the liquid-to-solid ratio of the ethanol to the sieve material B is 30-50 mL/g, and then stir at 50-80° C. for 2-7 h, followed by filtering, and drying the filtered solid at 60-150° C. for 2-24 h.
优选地,在步骤(1)中,控制粉碎物料中粒度>20目的占比为15-25重量%。Preferably, in step (1), the proportion of particles with a particle size of >20 mesh in the pulverized material is controlled to be 15-25% by weight.
优选地,在步骤(2)中,所述水与所述粒度为20-200目的粉碎物料的液固比为20-60mL/g。Preferably, in step (2), the liquid-to-solid ratio of the water to the pulverized material with a particle size of 20-200 mesh is 20-60 mL/g.
优选地,在步骤(2)中,所述搅拌的温度为50-70℃。Preferably, in step (2), the stirring temperature is 50-70°C.
优选地,在步骤(2)中,所述搅拌的时间为5-12h。 Preferably, in step (2), the stirring time is 5-12 hours.
优选地,在步骤(3)中,所述有机溶剂与所述筛上物A的液固比为10-60mL/g。Preferably, in step (3), the liquid-to-solid ratio of the organic solvent to the sieve oversize A is 10-60 mL/g.
优选地,在步骤(3)中,所述有机溶剂与所述筛上物A的液固比为20-40mL/g。Preferably, in step (3), the liquid-to-solid ratio of the organic solvent to the sieve oversize A is 20-40 mL/g.
优选地,在步骤(3)中,所述有机溶剂选自甲醇、乙醇、乙二醇、聚乙二醇、丙三醇、乙酸甲酯和乙酸乙酯中的一种或者两种以上。Preferably, in step (3), the organic solvent is selected from one or more of methanol, ethanol, ethylene glycol, polyethylene glycol, glycerol, methyl acetate and ethyl acetate.
优选地,在步骤(3)中,所述搅拌的温度为60-80℃。Preferably, in step (3), the stirring temperature is 60-80°C.
优选地,在步骤(4)中,所述烘干的温度为80-105℃,所述烘干的时间为4-16h。Preferably, in step (4), the drying temperature is 80-105° C., and the drying time is 4-16 h.
本发明的方法可以充分利用废弃风电叶片中的玻璃纤维,通过简单快捷的手段将风电叶片中的玻璃纤维富集,通过粉碎与搅拌相结合,回收玻璃纤维富集度较高的材料,从而有利于其后续回收利用。该工艺能耗较低且环保可行。The method of the present invention can make full use of the glass fibers in the waste wind turbine blades, enrich the glass fibers in the wind turbine blades by simple and quick means, and recover materials with high glass fiber enrichment by combining crushing and stirring, thereby facilitating their subsequent recycling. The process has low energy consumption and is environmentally friendly.
具体实施方式Detailed ways
以下对本发明的具体实施方式进行详细说明。应当理解的是,此处所描述的具体实施方式仅用于说明和解释本发明,并不用于限制本发明。The specific embodiments of the present invention are described in detail below. It should be understood that the specific embodiments described herein are only used to illustrate and explain the present invention, and are not used to limit the present invention.
在本文中所披露的范围的端点和任何值都不限于该精确的范围或值,这些范围或值应当理解为包含接近这些范围或值的值。对于数值范围来说,各个范围的端点值之间、各个范围的端点值和单独的点值之间,以及单独的点值之间可以彼此组合而得到一个或多个新的数 值范围,这些数值范围应被视为在本文中具体公开。The endpoints and any values of the ranges disclosed herein are not limited to the exact ranges or values, and these ranges or values should be understood to include values close to these ranges or values. For numerical ranges, the endpoint values of each range, the endpoint values of each range and the individual point values, and the individual point values can be combined with each other to obtain one or more new numerical values. Value ranges are intended to be considered specifically disclosed herein.
本发明提供一种富集废弃风电叶片中玻璃纤维的方法,所述方法包括以下步骤:The present invention provides a method for enriching glass fibers in waste wind turbine blades, the method comprising the following steps:
(1)将废弃风电叶片进行粉碎,得到粉碎物料,并控制粉碎物料中粒度>20目的占比为10-30重量%,粒度为20-200目的占比≥20重量%,然后进行筛分,并收集粒度为20-200目的粉碎物料;(1) crushing the discarded wind turbine blades to obtain crushed materials, and controlling the proportion of particles with a particle size of more than 20 mesh in the crushed materials to be 10-30% by weight, and the proportion of particles with a particle size of 20-200 mesh to be ≥20% by weight, and then screening and collecting the crushed materials with a particle size of 20-200 mesh;
(2)将收集得到的粒度为20-200目的粉碎物料与水混合,然后在40-80℃下搅拌2-16h,然后过140目筛,得到筛上物A;(2) mixing the collected pulverized material with a particle size of 20-200 mesh with water, stirring at 40-80° C. for 2-16 hours, and then passing through a 140-mesh sieve to obtain an oversize material A;
(3)将筛上物A与有机溶剂混合,然后在40-80℃下搅拌2-8h,然后过80目筛,得到筛上物B;(3) mixing the oversize A with an organic solvent, stirring at 40-80° C. for 2-8 hours, and then passing through an 80-mesh sieve to obtain an oversize B;
(4)将筛上物B与乙醇混合,所述乙醇与所述筛上物B的液固比为30-50mL/g,然后在50-80℃下搅拌2-7h,接着过滤,将过滤得到的固体在60-150℃下烘干2-24h。(4) Mix the sieve material B with ethanol, wherein the liquid-to-solid ratio of the ethanol to the sieve material B is 30-50 mL/g, and then stir at 50-80° C. for 2-7 h, followed by filtering, and drying the filtered solid at 60-150° C. for 2-24 h.
在本发明中,所述废弃风电叶片来源为风电厂退役或者意外导致不能使用的叶片,叶片构成主要为玻璃纤维组成的热固性复合材料(其余物质含量极少,可以忽略不计,且性质与主要成分差别不大),废弃风电叶片中玻璃纤维含量为50-85重量%,树脂含量为15-50重量%。In the present invention, the discarded wind turbine blades are blades that are retired from wind power plants or cannot be used due to accidents. The blades are mainly composed of a thermosetting composite material composed of glass fibers (the content of other substances is extremely small and can be ignored, and the properties are not much different from the main components). The glass fiber content in the discarded wind turbine blades is 50-85% by weight, and the resin content is 15-50% by weight.
在步骤(1)中,需要同时控制粉碎物料中,粒度>20目的占比为10-30重量%以及粒度为20-200目的占比≥20重量%。In step (1), it is necessary to simultaneously control the proportion of the pulverized material with a particle size of >20 mesh to be 10-30 weight % and the proportion of the particle size of 20-200 mesh to be ≥20 weight %.
在优选情况下,在步骤(1)中,控制粉碎物料中粒度>20目的占比为15-25重量%。在具体的实施方式中,在步骤(1)中,粉碎 物料中粒度>20目的占比可以为15重量%、16重量%、17重量%、18重量%、19重量%、20重量%、21重量%、22重量%、23重量%、24重量%或25重量%。In a preferred embodiment, in step (1), the proportion of the pulverized material with a particle size of >20 mesh is controlled to be 15-25% by weight. The proportion of particle size >20 mesh in the material can be 15 weight %, 16 weight %, 17 weight %, 18 weight %, 19 weight %, 20 weight %, 21 weight %, 22 weight %, 23 weight %, 24 weight % or 25 weight %.
在本发明步骤(2)中,所述水与所述粒度为20-200目的粉碎物料的液固比为20-60mL/g,优选为30-60mL/g,具体可以为30mL/g、35mL/g、40mL/g、45mL/g、50mL/g、55mL/g或60mL/g。In step (2) of the present invention, the liquid-to-solid ratio of the water to the pulverized material with a particle size of 20-200 mesh is 20-60 mL/g, preferably 30-60 mL/g, specifically 30 mL/g, 35 mL/g, 40 mL/g, 45 mL/g, 50 mL/g, 55 mL/g or 60 mL/g.
在优选情况下,在步骤(2)中,所述搅拌的温度为50-70℃。在具体的实施方式中,在步骤(2)中,所述搅拌的温度可以为50℃、55℃、60℃、65℃或70℃。Preferably, in step (2), the stirring temperature is 50-70° C. In a specific embodiment, in step (2), the stirring temperature can be 50° C., 55° C., 60° C., 65° C. or 70° C.
在优选情况下,在步骤(2)中,所述搅拌的时间为5-12h。在具体的实施方式中,在步骤(2)中,所述搅拌的时间可以为5h、6h、7h、8h、9h、10h、11h或12h。In a preferred embodiment, in step (2), the stirring time is 5-12 hours. In a specific embodiment, in step (2), the stirring time can be 5 hours, 6 hours, 7 hours, 8 hours, 9 hours, 10 hours, 11 hours or 12 hours.
在本发明步骤(3)中,所述有机溶剂与所述筛上物A的液固比为10-60mL/g,优选为20-40mL/g,具体可以为20mL/g、25mL/g、30mL/g、35mL/g或40mL/g。In step (3) of the present invention, the liquid-to-solid ratio of the organic solvent to the sieve material A is 10-60 mL/g, preferably 20-40 mL/g, specifically 20 mL/g, 25 mL/g, 30 mL/g, 35 mL/g or 40 mL/g.
优选地,在步骤(3)中,所述有机溶剂选自甲醇、乙醇、乙二醇、聚乙二醇、丙三醇、乙酸甲酯和乙酸乙酯中的一种或者两种以上。Preferably, in step (3), the organic solvent is selected from one or more of methanol, ethanol, ethylene glycol, polyethylene glycol, glycerol, methyl acetate and ethyl acetate.
进一步优选地,在步骤(3)中,所述搅拌的温度为60-80℃。具体可以为60℃、65℃、70℃、75℃或80℃。More preferably, in step (3), the stirring temperature is 60-80°C, and specifically can be 60°C, 65°C, 70°C, 75°C or 80°C.
在具体的实施方式中,在步骤(3)中,所述搅拌的时间可以为2h、3h、4h、5h、6h、7h或8h。In a specific embodiment, in step (3), the stirring time can be 2h, 3h, 4h, 5h, 6h, 7h or 8h.
在本发明步骤(3)中,为了避免后续有机组分和粉碎料中出现 聚合团聚等现象,因此在优选情况下,在搅拌完成后不用等到冷却到室温,而是在搅拌结束后立即直接过80目筛。In step (3) of the present invention, in order to avoid the subsequent organic components and crushed materials Therefore, in a preferred embodiment, after the stirring is completed, the mixture does not need to be cooled to room temperature, but is directly passed through an 80-mesh sieve immediately after the stirring is completed.
在具体的实施方式中,在步骤(4)中,所述乙醇与所述筛上物B的液固比可以为30mL/g、35mL/g、40mL/g、45mL/g或50mL/g。In a specific embodiment, in step (4), the liquid-to-solid ratio of the ethanol to the oversize material B can be 30 mL/g, 35 mL/g, 40 mL/g, 45 mL/g or 50 mL/g.
在具体的实施方式中,在步骤(4)中,所述搅拌的温度可以为50℃、55℃、60℃、65℃、70℃、75℃或80℃,所述搅拌的时间可以为2h、3h、4h、5h、6h或7h。In a specific embodiment, in step (4), the stirring temperature can be 50°C, 55°C, 60°C, 65°C, 70°C, 75°C or 80°C, and the stirring time can be 2h, 3h, 4h, 5h, 6h or 7h.
进一步优选地,步骤(4)中,所述烘干的温度为80-105℃,所述烘干的时间为4-16h。具体地,所述烘干的温度可以为80℃、85℃、90℃、95℃、100℃或105℃,所述烘干的时间可以为4h、7h、10h、13h或16h。Further preferably, in step (4), the drying temperature is 80-105°C, and the drying time is 4-16h. Specifically, the drying temperature can be 80°C, 85°C, 90°C, 95°C, 100°C or 105°C, and the drying time can be 4h, 7h, 10h, 13h or 16h.
发明人经过大量实验研究以及充分考虑玻璃纤维和树脂在破碎阶段被破碎程度的差异性,并充分考虑到纤维和树脂在溶液中的团聚差异性,通过探索得到上述工艺条件。The inventors obtained the above process conditions through a large number of experimental studies and full consideration of the differences in the degree of crushing of glass fibers and resins in the crushing stage, as well as the differences in the agglomeration of fibers and resins in the solution.
本发明的方法可以充分利用废弃风电叶片中的玻璃纤维,通过简单快捷的手段将风电叶片中的玻璃纤维富集,通过整体粉碎与搅拌相结合,回收玻璃纤维富集度较高的材料,能从而有利于其后续回收利用。该工艺能耗较低且环保可行。The method of the present invention can make full use of the glass fibers in the waste wind turbine blades, enrich the glass fibers in the wind turbine blades by simple and quick means, and recover materials with high glass fiber enrichment by combining overall crushing and stirring, which can facilitate their subsequent recycling. The process has low energy consumption and is environmentally friendly.
本方法通过将纤维进一步富集,提高产品玻璃纤维含量,适当降低树脂含量可以极大的提升产物的应有领域和使用范围,达到了低成本的资源化目的。This method can greatly improve the applicable fields and application scope of the product by further enriching the fiber, increasing the glass fiber content of the product, and appropriately reducing the resin content, thereby achieving the purpose of low-cost resource utilization.
以下将通过实施例对本发明进行详细描述,但本发明所述的方法 不仅限于此。The present invention will be described in detail below by way of examples. It’s not just that.
以下实施例和对比例中所用的废弃风电叶片来自于国内某风力发电厂,其中玻璃纤维以及树脂的含量见表1。The discarded wind turbine blades used in the following examples and comparative examples come from a domestic wind power plant, and the contents of glass fiber and resin are shown in Table 1.
实施例1Example 1
(1)将废弃风电叶片进行整体粉碎,得到粉碎物料,并控制粉碎物料中粒度>20目的占比为21.3重量%,粒度为20-200目的占比为35.47重量%,然后进行筛分,并收集粒度为20-200目的粉碎物料;(1) crushing the discarded wind turbine blades as a whole to obtain crushed materials, and controlling the proportion of particles with a particle size of more than 20 mesh to be 21.3% by weight, and the proportion of particles with a particle size of 20-200 mesh to be 35.47% by weight, and then screening and collecting the crushed materials with a particle size of 20-200 mesh;
(2)将收集得到的粒度为20-200目的粉碎物料与水混合(水与粒度为20-200目的粉碎物料的液固比为40mL/g),然后在50℃下搅拌8h,然后过140目筛,得到筛上物A;(2) mixing the collected pulverized material with a particle size of 20-200 mesh with water (the liquid-to-solid ratio of water to the pulverized material with a particle size of 20-200 mesh is 40 mL/g), stirring at 50° C. for 8 h, and then passing through a 140-mesh sieve to obtain an oversize material A;
(3)将筛上物A与甲醇混合(甲醇与筛上物A的液固比为30mL/g),然后在60℃下搅拌4h,然后立即趁热直接过80目筛,得到筛上物B;(3) Mix the oversize A with methanol (the liquid-to-solid ratio of methanol to oversize A is 30 mL/g), then stir at 60° C. for 4 h, and then immediately pass through an 80-mesh sieve while hot to obtain oversize B;
(4)将筛上物B与乙醇混合,乙醇与筛上物B的液固比为40mL/g,然后在60℃下搅拌5h,接着过滤,将过滤得到的固体在80℃下烘干12h。(4) The oversize material B was mixed with ethanol at a liquid-to-solid ratio of ethanol to oversize material B of 40 mL/g, and then stirred at 60° C. for 5 h, followed by filtration, and the filtered solid was dried at 80° C. for 12 h.
实施例2Example 2
(1)将废弃风电叶片进行整体粉碎,得到粉碎物料,并控制粉碎物料中粒度>20目的占比为18.9重量%,粒度为20-200目的占比为31.66重量%,然后进行筛分,并收集粒度为20-200目的粉碎物料; (1) crushing the discarded wind turbine blades as a whole to obtain crushed materials, and controlling the proportion of particles with a particle size of more than 20 mesh to be 18.9% by weight, and the proportion of particles with a particle size of 20-200 mesh to be 31.66% by weight, and then screening and collecting the crushed materials with a particle size of 20-200 mesh;
(2)将收集得到的粒度为20-200目的粉碎物料与水混合(水与粒度为20-200目的粉碎物料的液固比为40mL/g),然后在60℃下搅拌8h,然后过140目筛,得到筛上物A;(2) mixing the collected pulverized material with a particle size of 20-200 mesh with water (the liquid-to-solid ratio of water to the pulverized material with a particle size of 20-200 mesh is 40 mL/g), stirring at 60° C. for 8 h, and then passing through a 140-mesh sieve to obtain an oversize material A;
(3)将筛上物A与乙二醇混合(乙二醇与筛上物A的液固比为30mL/g),然后在70℃下搅拌4h,然后立即趁热直接过80目筛,得到筛上物B;(3) Mixing the oversize A with ethylene glycol (the liquid-to-solid ratio of ethylene glycol to oversize A is 30 mL/g), stirring at 70° C. for 4 h, and then immediately passing the mixture through an 80-mesh sieve while hot to obtain oversize B;
(4)将筛上物B与乙醇混合,乙醇与筛上物B的液固比为40mL/g,然后在70℃下搅拌6h,接着过滤,将过滤得到的固体在80℃下烘干10h。(4) The oversize material B was mixed with ethanol at a liquid-to-solid ratio of ethanol to oversize material B of 40 mL/g, and then stirred at 70° C. for 6 h, followed by filtration, and the filtered solid was dried at 80° C. for 10 h.
实施例3Example 3
(1)将废弃风电叶片进行整体粉碎,得到粉碎物料,并控制粉碎物料中粒度>20目的占比为15.6重量%,粒度为20-200目的占比为36.76重量%,然后进行筛分,并收集粒度为20-200目的粉碎物料;(1) crushing the discarded wind turbine blades as a whole to obtain crushed materials, and controlling the proportion of particles with a particle size of more than 20 mesh to be 15.6% by weight, and the proportion of particles with a particle size of 20-200 mesh to be 36.76% by weight in the crushed materials, and then screening and collecting the crushed materials with a particle size of 20-200 mesh;
(2)将收集得到的粒度为20-200目的粉碎物料与水混合(水与粒度为20-200目的粉碎料的液固比为30mL/g),然后在60℃下搅拌8h,然后过140目筛,得到筛上物A;(2) mixing the collected pulverized material with a particle size of 20-200 mesh with water (the liquid-to-solid ratio of water to the pulverized material with a particle size of 20-200 mesh is 30 mL/g), stirring at 60° C. for 8 h, and then passing through a 140-mesh sieve to obtain an oversize material A;
(3)将筛上物A与乙酸乙酯混合(乙酸乙酯与所述筛上物A的液固比为20mL/g),然后在70℃下搅拌4h,然后立即趁热直接过80目筛,得到筛上物B,(3) The oversize A was mixed with ethyl acetate (the liquid-to-solid ratio of ethyl acetate to the oversize A was 20 mL/g), and then stirred at 70° C. for 4 h, and then immediately passed through an 80-mesh sieve while hot to obtain an oversize B.
(4)将筛上物B与乙醇混合,乙醇与筛上物B的液固比为35mL/g,然后在80℃下搅拌6h,接着过滤,将过滤得到的固体在80℃下烘干 8h。(4) Mix the sieve material B with ethanol, the liquid-to-solid ratio of ethanol to the sieve material B is 35 mL/g, then stir at 80°C for 6 h, filter, and dry the filtered solid at 80°C 8h.
实施例4Example 4
(1)将废弃风电叶片进行整体粉碎,得到粉碎物料,并控制粉碎物料中粒度>20目的占比为22.4重量%,粒度为20-200目的占比为34.33重量%,然后进行筛分,并收集粒度为20-200目的粉碎物料;(1) crushing the discarded wind turbine blades as a whole to obtain crushed materials, and controlling the proportion of particles with a particle size of more than 20 mesh to be 22.4% by weight, and the proportion of particles with a particle size of 20-200 mesh to be 34.33% by weight, and then screening and collecting the crushed materials with a particle size of 20-200 mesh;
(2)将收集得到的粒度为20-200目的粉碎物料与水混合(水与粒度为20-200目的粉碎料的液固比为50mL/g),然后在65℃下搅拌8h,然后过140目筛,得到筛上物A;(2) mixing the collected pulverized material with a particle size of 20-200 mesh with water (the liquid-to-solid ratio of water to the pulverized material with a particle size of 20-200 mesh is 50 mL/g), stirring at 65° C. for 8 h, and then passing through a 140-mesh sieve to obtain an oversize material A;
(3)将筛上物A与乙二醇混合(乙二醇与所述筛上物A的液固比为40mL/g),然后在60℃下搅拌6h,然后立即趁热直接过80目筛,得到筛上物B;(3) mixing the oversize A with ethylene glycol (the liquid-to-solid ratio of ethylene glycol to the oversize A is 40 mL/g), stirring at 60° C. for 6 h, and then immediately passing the oversize B through an 80-mesh sieve while hot to obtain an oversize B;
(4)将筛上物B与乙醇混合,乙醇与筛上物B的液固比为40mL/g,然后在70℃下搅拌5h,接着过滤,将过滤得到的固体在100℃下烘干4h。(4) The oversize material B was mixed with ethanol at a liquid-to-solid ratio of ethanol to oversize material B of 40 mL/g, and then stirred at 70° C. for 5 h, followed by filtration, and the filtered solid was dried at 100° C. for 4 h.
对比例1Comparative Example 1
按照实施例1的方法进行实施,与之不同的是,在步骤(1)中,控制粉碎物料中粒度>20目的占比为2.48重量%,粒度为20-200目的占比为41.22重量%,然后进行筛分,并收集粒度为20-200目的粉碎物料。 The method of Example 1 is followed, except that in step (1), the proportion of particles with a particle size of >20 mesh in the crushed material is controlled to be 2.48% by weight, and the proportion of particles with a particle size of 20-200 mesh is controlled to be 41.22% by weight, and then screening is performed to collect the crushed material with a particle size of 20-200 mesh.
对比例2Comparative Example 2
按照实施例1的方法进行实施,与之不同的是,在步骤(1)中,控制粉碎后的物料中粒度>20目的占比为43.86重量%,粒度为20-200目的占比为22.43重量%,然后进行筛分,并收集粒度为20-200目的粉碎物料。The method of Example 1 is followed, except that in step (1), the proportion of particles with a particle size of >20 mesh in the crushed material is controlled to be 43.86% by weight, and the proportion of particles with a particle size of 20-200 mesh is controlled to be 22.43% by weight, and then screening is performed to collect the crushed material with a particle size of 20-200 mesh.
对比例3Comparative Example 3
(1)将废弃风电叶片进行整体粉碎,得到粉碎物料,并控制粉碎物料中粒度>20目的占比为21.3重量%,粒度为20-200目的占比为26.26重量%,然后进行筛分,并收集粒度为20-200目的粉碎物料;(1) crushing the discarded wind turbine blades as a whole to obtain crushed materials, and controlling the proportion of particles with a particle size of more than 20 mesh to be 21.3% by weight, and the proportion of particles with a particle size of 20-200 mesh to be 26.26% by weight, and then screening and collecting the crushed materials with a particle size of 20-200 mesh;
(2)将收集得到的粒度为20-200目的粉碎物料与水混合(水与粒度为20-200目的粉碎物料的液固比为40mL/g),然后在50℃下搅拌8h,然后过140目筛,得到筛上物A,将筛上物A直接在80℃下烘干12h。(2) The collected pulverized material with a particle size of 20-200 mesh was mixed with water (the liquid-to-solid ratio of water to the pulverized material with a particle size of 20-200 mesh was 40 mL/g), and then stirred at 50° C. for 8 h, and then passed through a 140-mesh sieve to obtain an oversize material A, which was directly dried at 80° C. for 12 h.
测试例1Test Example 1
分别检测实施例1-4和对比例1-3中得到的产品中玻璃纤维的含量The content of glass fiber in the products obtained in Examples 1-4 and Comparative Examples 1-3 was detected respectively.
玻璃纤维的含量的检测方法为:准确称量样品重量M1,在600焙烧3h后,称量重量M2,玻璃纤维的含量为R=M2/M1*100%。The method for detecting the content of glass fiber is: accurately weigh the sample weight M1, and after calcining at 600°C for 3 hours, weigh the weight M2. The content of glass fiber is R=M2/M1*100%.
结果如表1所示。The results are shown in Table 1.
表1
Table 1
通过表1的结果可以看出,通过本方法快速富集后,得到的产品中玻璃纤维含量已经在85%以上,含量很高,可以直接用于建材等领域的使用。It can be seen from the results in Table 1 that after rapid enrichment by this method, the glass fiber content in the obtained product is already above 85%, which is very high and can be directly used in the fields of building materials and the like.
以上详细描述了本发明的优选实施方式,但是,本发明并不限于此。在本发明的技术构思范围内,可以对本发明的技术方案进行多种简单变型,包括各个技术特征以任何其它的合适方式进行组合,这些简单变型和组合同样应当视为本发明所公开的内容,均属于本发明的保护范围。 The preferred embodiments of the present invention are described in detail above, but the present invention is not limited thereto. Within the technical concept of the present invention, the technical solution of the present invention can be subjected to a variety of simple modifications, including the combination of various technical features in any other suitable manner, and these simple modifications and combinations should also be regarded as the contents disclosed by the present invention and belong to the protection scope of the present invention.

Claims (9)

  1. 一种富集废弃风电叶片中玻璃纤维的方法,其特征在于,所述方法的步骤如下:A method for enriching glass fibers in waste wind turbine blades, characterized in that the method comprises the following steps:
    (1)将废弃风电叶片进行粉碎,得到粉碎物料,并控制粉碎物料中粒度>20目的占比为15-25重量%,粒度为20-200目的占比≥20重量%,然后进行筛分,并收集粒度为20-200目的粉碎物料;(1) crushing the discarded wind turbine blades to obtain crushed materials, and controlling the proportion of particles with a particle size of more than 20 mesh in the crushed materials to be 15-25% by weight, and the proportion of particles with a particle size of 20-200 mesh to be ≥20% by weight, and then screening and collecting the crushed materials with a particle size of 20-200 mesh;
    (2)将收集得到的粒度为20-200目的粉碎物料与水混合,然后在40-80℃下搅拌2-16h,然后过140目筛,得到筛上物A;(2) mixing the collected pulverized material with a particle size of 20-200 mesh with water, stirring at 40-80° C. for 2-16 hours, and then passing through a 140-mesh sieve to obtain an oversize material A;
    (3)将筛上物A与有机溶剂混合,然后在40-80℃下搅拌2-8h,然后过80目筛,得到筛上物B;(3) mixing the oversize A with an organic solvent, stirring at 40-80° C. for 2-8 hours, and then passing through an 80-mesh sieve to obtain an oversize B;
    (4)将筛上物B与乙醇混合,所述乙醇与所述筛上物B的液固比为30-50mL/g,然后在50-80℃下搅拌2-7h,接着过滤,将过滤得到的固体在60-150℃下烘干2-24h。(4) Mix the sieve material B with ethanol, wherein the liquid-to-solid ratio of the ethanol to the sieve material B is 30-50 mL/g, and then stir at 50-80° C. for 2-7 h, followed by filtering, and drying the filtered solid at 60-150° C. for 2-24 h.
  2. 根据权利要求1所述的方法,其特征在于,在步骤(2)中,所述水与所述粒度为20-200目的粉碎物料的液固比为20-60mL/g。The method according to claim 1 is characterized in that in step (2), the liquid-to-solid ratio of the water to the crushed material with a particle size of 20-200 mesh is 20-60 mL/g.
  3. 根据权利要求1所述的方法,其特征在于,在步骤(2)中,所述搅拌的温度为50-70℃。The method according to claim 1, characterized in that in step (2), the stirring temperature is 50-70°C.
  4. 根据权利要求1或3所述的方法,其特征在于,在步骤(2)中,所述搅拌的时间为5-12h。 The method according to claim 1 or 3, characterized in that, in step (2), the stirring time is 5-12 hours.
  5. 根据权利要求1所述的方法,其特征在于,在步骤(3)中,所述有机溶剂与所述筛上物A的液固比为10-60mL/g。The method according to claim 1, characterized in that in step (3), the liquid-to-solid ratio of the organic solvent to the sieve oversize A is 10-60 mL/g.
  6. 根据权利要求1所述的方法,其特征在于,在步骤(3)中,所述有机溶剂与所述筛上物A的液固比为20-40mL/g。The method according to claim 1, characterized in that in step (3), the liquid-to-solid ratio of the organic solvent to the sieve oversize A is 20-40 mL/g.
  7. 根据权利要求1或5所述的方法,其特征在于,在步骤(3)中,所述有机溶剂选自甲醇、乙醇、乙二醇、聚乙二醇、丙三醇、乙酸甲酯和乙酸乙酯中的一种或者两种以上。The method according to claim 1 or 5, characterized in that in step (3), the organic solvent is selected from one or more of methanol, ethanol, ethylene glycol, polyethylene glycol, glycerol, methyl acetate and ethyl acetate.
  8. 根据权利要求1所述的方法,其特征在于,在步骤(3)中,所述搅拌的温度为60-80℃。The method according to claim 1, characterized in that in step (3), the stirring temperature is 60-80°C.
  9. 根据权利要求1所述的方法,其特征在于,在步骤(4)中,所述烘干的温度为80-105℃,所述烘干的时间为4-16h。 The method according to claim 1 is characterized in that, in step (4), the drying temperature is 80-105°C and the drying time is 4-16h.
PCT/CN2023/096219 2022-11-14 2023-05-25 Method for enriching glass fibers in waste wind turbine blades WO2024103672A1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CN202211417649.4A CN115447028B (en) 2022-11-14 2022-11-14 Method for enriching glass fibers in waste wind power blades
CN202211417649.4 2022-11-14

Publications (1)

Publication Number Publication Date
WO2024103672A1 true WO2024103672A1 (en) 2024-05-23

Family

ID=84295590

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/CN2023/096219 WO2024103672A1 (en) 2022-11-14 2023-05-25 Method for enriching glass fibers in waste wind turbine blades

Country Status (2)

Country Link
CN (1) CN115447028B (en)
WO (1) WO2024103672A1 (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115447028B (en) * 2022-11-14 2023-02-07 国能龙源环保有限公司 Method for enriching glass fibers in waste wind power blades
CN116253553B (en) * 2023-05-16 2023-07-28 国能龙源环保有限公司 Method for preparing concrete by utilizing waste materials of wind turbine generator
CN116274307B (en) * 2023-05-17 2023-08-01 国能龙源环保有限公司 Method for recycling waste wind power blades
CN116274288B (en) * 2023-05-17 2023-08-08 国能龙源环保有限公司 Method for recycling waste wind power blades
CN117021420B (en) * 2023-10-08 2024-02-02 国能龙源环保有限公司 Method for recycling bassa wood from waste wind power blades

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5476628A (en) * 1993-09-11 1995-12-19 Basf Aktiengesellschaft GMT sheet material produced from GMT recyclate
CN105881775A (en) * 2016-02-25 2016-08-24 吉林重通成飞新材料股份公司 Wind power blade recovery treatment method
CN107082557A (en) * 2016-02-15 2017-08-22 山东理工大学 A kind of glass fibre reinforced composion castoff regenerative glass fibre method
CN107082586A (en) * 2016-02-15 2017-08-22 山东理工大学 A kind of low energy consumption comprehensive utilizes fiberglass and the method for red mud solid waste
CN107415088A (en) * 2017-05-03 2017-12-01 清华大学 Fiber reinforced thermosetting resin material recovery preparation method for material
CN208343226U (en) * 2017-12-11 2019-01-08 上海越科新材料股份有限公司 A kind of large-scale wind generating blade recovery and processing system
CN112693036A (en) * 2020-12-08 2021-04-23 河北中科同创科技发展有限公司 Pretreatment method of glass fiber reinforced plastic leftover material
CN112706322A (en) * 2020-12-08 2021-04-27 河北中科同创科技发展有限公司 Treatment method of glass fiber reinforced plastic leftover material
CN115447028A (en) * 2022-11-14 2022-12-09 国能龙源环保有限公司 Method for enriching glass fibers in waste wind power blades

Family Cites Families (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4151154A (en) * 1976-09-29 1979-04-24 Union Carbide Corporation Silicon treated surfaces
JP2003001140A (en) * 2001-06-18 2003-01-07 Kubota Corp Manufacturing method for waste frp powder
EP2810276B1 (en) * 2012-01-31 2017-11-22 Eastman Chemical Company Processes to produce short cut microfibers
DE102013002005A1 (en) * 2013-02-06 2014-08-07 Fraunhofer-Gesellschaft zur Förderung der angewandten Forschung e.V. Process for the recovery of fibers from components and products made of plastic fiber composite materials
KR101801788B1 (en) * 2015-12-11 2017-11-28 한국과학기술연구원 Method and apparatus for recovering fiber assembly from thermosetting resin composite materials and recovered fiber assembly
AU2017247711B2 (en) * 2016-04-05 2019-05-16 Composite Tech Holdings Limited Recycling of polymer matrix composite
CN110181717B (en) * 2019-07-10 2024-06-04 吉林重通成飞新材料股份公司 Wind power blade material screening equipment and wind power blade material screening method
CN114775287B (en) * 2022-05-20 2023-07-21 济南大学 Modified waste wind power blade regenerated fiber and preparation method thereof

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5476628A (en) * 1993-09-11 1995-12-19 Basf Aktiengesellschaft GMT sheet material produced from GMT recyclate
CN107082557A (en) * 2016-02-15 2017-08-22 山东理工大学 A kind of glass fibre reinforced composion castoff regenerative glass fibre method
CN107082586A (en) * 2016-02-15 2017-08-22 山东理工大学 A kind of low energy consumption comprehensive utilizes fiberglass and the method for red mud solid waste
CN105881775A (en) * 2016-02-25 2016-08-24 吉林重通成飞新材料股份公司 Wind power blade recovery treatment method
CN107415088A (en) * 2017-05-03 2017-12-01 清华大学 Fiber reinforced thermosetting resin material recovery preparation method for material
CN208343226U (en) * 2017-12-11 2019-01-08 上海越科新材料股份有限公司 A kind of large-scale wind generating blade recovery and processing system
CN112693036A (en) * 2020-12-08 2021-04-23 河北中科同创科技发展有限公司 Pretreatment method of glass fiber reinforced plastic leftover material
CN112706322A (en) * 2020-12-08 2021-04-27 河北中科同创科技发展有限公司 Treatment method of glass fiber reinforced plastic leftover material
CN115447028A (en) * 2022-11-14 2022-12-09 国能龙源环保有限公司 Method for enriching glass fibers in waste wind power blades

Also Published As

Publication number Publication date
CN115447028A (en) 2022-12-09
CN115447028B (en) 2023-02-07

Similar Documents

Publication Publication Date Title
WO2024103672A1 (en) Method for enriching glass fibers in waste wind turbine blades
CN102050919B (en) Supported imidazole ion liquid cross-linked polymer nano particles and preparation and application thereof
CN104600390B (en) Method for preparing magnetostriction material by utilizing spent lithium ion batteries
CN101572329A (en) Method for recovering lithium-ion battery cathode materials
CN104326907A (en) Method for degrading and recycling unsaturated polyester resin material
CN115556271A (en) Method for separating and enriching resin in waste wind power blade
CN101570347B (en) Method for recovering lithium-ion battery cathode materials
CN105314693A (en) Method for preparing compound water purifying agent from waste aluminum ash
CN102690632A (en) Method for preparing environment-friendly snow melting agent by using pyroligneous liquid
CN205528470U (en) Building rubbish preparation regeneration building material's production facility
CN112126413A (en) Composite phase change material and preparation method thereof
CN103769045A (en) Preparation method for fly-ash-based adsorption material with high performances
CN104098084B (en) The preparation method of the controlled carbon nanotube paper of a kind of shape and size
CN102584906A (en) Extracting method of fulvic acid
CN107158800A (en) A kind of modifying aramid fiber nanofiber/polyphenylene sulfide fibre composite dedusting filtrate and preparation method
CN103319565A (en) Clean and high-efficiency process for producing diosgenin
CN109119714B (en) Method for separating and recovering positive active material in lithium ion battery
CN113045769A (en) Method for preparing lignosulfonate by using sulfate pulping waste liquid and application
CN110975812B (en) Tea saponin hollow carbon spheres, preparation method thereof and application thereof in heavy metal adsorption
CN105097291B (en) A kind of nitrogen boron codope gelatin-based two dimension carbon plate and preparation method thereof
CN109881517B (en) Method for quickly liquefying rice straws in high-pressure environment
CN105215349B (en) Magnetic composite micro-wire and preparation method thereof
CN107055507A (en) A kind of preparation method of carbon molecular sieve
CN103554534A (en) Preparation method of wood fiber biomass film
CN113851625A (en) Molybdenum disulfide graphite composite negative electrode material and preparation method thereof

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 23890116

Country of ref document: EP

Kind code of ref document: A1