CN107043233A - Process for preparing alkali-based geopolymer ecological material - Google Patents
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- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B28/00—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
- C04B28/006—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing mineral polymers, e.g. geopolymers of the Davidovits type
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- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2201/00—Mortars, concrete or artificial stone characterised by specific physical values
- C04B2201/20—Mortars, concrete or artificial stone characterised by specific physical values for the density
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- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2201/00—Mortars, concrete or artificial stone characterised by specific physical values
- C04B2201/50—Mortars, concrete or artificial stone characterised by specific physical values for the mechanical strength
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- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P40/00—Technologies relating to the processing of minerals
- Y02P40/10—Production of cement, e.g. improving or optimising the production methods; Cement grinding
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
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Abstract
本发明涉及制备碱基地聚物生态材料的工艺。取适量高岭土煅烧磨细过筛得偏高岭土;取生活垃圾焚烧飞灰50~70份,偏高岭土30~50份,激发剂10~20份,干料混匀后掺10~30份水,搅拌均匀后,将混料注入模具振实,然后模具置于干燥箱中干养护后拆模,最后将拆模后的砖体继续置于30~80℃的干燥箱中养护12~21d后得碱基地聚物生态材料。利用偏高岭土和生活垃圾焚烧飞灰,生产新型环保功能材料。能因地制宜地利用工业废弃物,有效保护水土资源,控制环境污染。具有重大的环境、经济和社会效益。The invention relates to a process for preparing an alkali base polymer ecological material. Take an appropriate amount of kaolin, calcined, grind and sieve to obtain metakaolin; take 50-70 parts of domestic waste incineration fly ash, 30-50 parts of metakaolin, 10-20 parts of activator, mix the dry material with 10-30 parts of water, and stir After uniformity, inject the mixture into the mold and vibrate, then place the mold in a drying oven for dry curing and remove the mold, and finally place the removed brick body in a drying oven at 30-80°C for 12-21 days to obtain alkali Base polymer ecological material. Utilize metakaolin and domestic waste incineration fly ash to produce new environmentally friendly functional materials. Can use industrial waste according to local conditions, effectively protect water and soil resources, and control environmental pollution. It has significant environmental, economic and social benefits.
Description
技术领域technical field
本发明涉及一种固体废物的资源化处置,具体是涉及一种生活垃圾焚烧飞灰制备碱基地聚物生态材料的工艺。The invention relates to a resource disposal of solid waste, in particular to a process for preparing alkaline-based polymer ecological materials from domestic waste incineration fly ash.
背景技术Background technique
在生活垃圾焚烧过程中,其尾气处理环节会产生约占垃圾焚烧总量5%左右的飞灰,据估算,我国生活垃圾焚烧飞灰年产量约500万吨。飞灰一般呈灰白色或深灰色,粒径小于300μm,含水率5%~15%,热灼减率为10%~15%,颗粒形态多样化。飞灰给环境带来的污染主要有重金属污染、二噁英污染和溶解盐污染。飞灰中的主要重金属污染元素为Pb、Cd和Ni。垃圾焚烧过程中由于垃圾组分、通气量等原因造成焚烧不完全,在飞灰颗粒中富集一定量剧毒的二噁英和呋喃(PCDD/DFs)类有机污染物,在生活垃圾焚烧飞灰的运输、贮存、处理和处置中,将对生态环境构成威胁,对人类健康造成危害。In the process of domestic waste incineration, the tail gas treatment process will produce fly ash which accounts for about 5% of the total waste incineration. It is estimated that the annual output of domestic waste incineration fly ash in my country is about 5 million tons. Fly ash is generally off-white or dark gray, with a particle size of less than 300 μm, a moisture content of 5% to 15%, a heat loss rate of 10% to 15%, and various particle shapes. The pollution caused by fly ash to the environment mainly includes heavy metal pollution, dioxin pollution and dissolved salt pollution. The main heavy metal pollution elements in fly ash are Pb, Cd and Ni. During the waste incineration process, due to incomplete incineration due to waste components, ventilation volume, etc., a certain amount of highly toxic dioxin and furan (PCDD/DFs) organic pollutants are enriched in the fly ash particles. During transportation, storage, handling and disposal, it will pose a threat to the ecological environment and cause harm to human health.
生活垃圾焚烧飞灰资源化利用是解决其处理难题的唯一途径。生活垃圾焚烧飞灰的资源化利用必须从资源利用和环境影响两方面予以考虑。在目前的研究中,生活垃圾焚烧飞灰的资源化利用需要考虑一下3各因素:(1)使用性能和成本。良好的使用性能和低成本是资源化利用和市场化推广的必要条件。(2)加工适应性。这主要由飞灰的物理化学性质决定。(3)符合环境标准且具有长期稳定性。The resource utilization of domestic waste incineration fly ash is the only way to solve the problem of its disposal. The resource utilization of domestic waste incineration fly ash must be considered from two aspects: resource utilization and environmental impact. In the current research, three factors need to be considered for resource utilization of MSW incineration fly ash: (1) Performance and cost. Good performance and low cost are necessary conditions for resource utilization and market promotion. (2) Processing adaptability. This is mainly determined by the physical and chemical properties of fly ash. (3) Comply with environmental standards and have long-term stability.
生活垃圾焚烧飞灰的主要成分属于CaO-SiO2-Al2O3-Fe2O3体系,加入某些掺合料经药剂激发后,会发生非晶态结构的解聚反应和解聚反应产生的单聚体的缩聚反应,并形成类沸石结构的地聚物,具有较好的吸附性,可以对包括重金属在内的污染物起到一定的处理效果,满足环保要求。因此可以用生活垃圾焚烧飞灰制备经济环保的碱基地聚物生态材料。The main components of domestic waste incineration fly ash belong to the CaO-SiO 2 -Al 2 O 3 -Fe 2 O 3 system. After some admixtures are added and stimulated by chemicals, depolymerization reactions of amorphous structures and depolymerization reactions will occur. The polycondensation reaction of monomers, and the formation of geopolymers with zeolite structure, has good adsorption, can play a certain treatment effect on pollutants including heavy metals, and meet environmental protection requirements. Therefore, the economical and environment-friendly alkali-based polymer ecological materials can be prepared from domestic waste incineration fly ash.
发明内容Contents of the invention
本发明的目的在于克服现有技术的不足,提出一种制备碱基地聚物生态材料的工艺,本发明利用生活垃圾焚烧飞灰以及偏高岭土生产新型生态材料,实现“变废为宝”。具有重大的环境、经济和社会效益。The purpose of the present invention is to overcome the deficiencies of the prior art, and propose a process for preparing alkali-based polymer ecological materials. The present invention utilizes domestic waste incineration fly ash and metakaolin to produce new ecological materials, and realizes "turning waste into treasure". It has significant environmental, economic and social benefits.
本发明的技术方案为:一种制备碱基地聚物生态材料的工艺,具体步骤如下:The technical solution of the present invention is: a process for preparing an alkali-based polymer ecological material, and the specific steps are as follows:
⑴、取适量高岭土,在一定温度下煅烧后制得偏高岭土,研磨过筛备用;(1) Take an appropriate amount of kaolin, calcined at a certain temperature to obtain metakaolin, grind and sieve for later use;
⑵、称取垃圾焚烧飞灰50~70份、偏高岭土(干基)30~50份、激发剂10~20份,混合均匀;(2) Weigh 50-70 parts of waste incineration fly ash, 30-50 parts of metakaolin (dry basis), 10-20 parts of activator, and mix well;
⑶、加入10~30份水,置于搅拌机中搅拌均匀;(3) Add 10-30 parts of water, put in a mixer and stir evenly;
⑷、浆体注入模具中振实;⑷, inject the slurry into the mold and vibrate;
⑸、将注浆完毕的模具送至干燥箱,在30~80℃下干养护12~48小时后拆模;⑸. Send the mold after grouting to the drying box, and remove the mold after dry curing at 30-80°C for 12-48 hours;
⑹、拆模后的块体继续在30~80℃下,干养护12~21d后得碱基地聚物生态材料。⑹. After removing the formwork, continue to dry-cure the blocks at 30-80°C for 12-21 days to obtain an alkali-based polymer ecological material.
优选步骤(1)中所述的煅烧稳定温度为700~900℃,煅烧时间为0.5~2h。优选步骤(1)所述的研磨过筛为过100目筛。Preferably, the stable calcination temperature in step (1) is 700-900° C., and the calcination time is 0.5-2 h. Preferably, the grinding and sieving described in step (1) is passing through a 100 mesh sieve.
优选步骤(2)所述的特征在于掺和料为偏高岭土。优选步骤(2)中所述的激发剂为硅酸钠、氢氧化钠或氢氧化钾中的一种或多种。The preferred step (2) is characterized in that the admixture is metakaolin. Preferably, the activator described in step (2) is one or more of sodium silicate, sodium hydroxide or potassium hydroxide.
优选步骤(3)中的搅拌速度为50~200转/分钟,搅拌时间为20~30min。优选步骤(4)中的振实频率为30~50次/分钟,振实时间为2~6min。Preferably, the stirring speed in step (3) is 50-200 rpm, and the stirring time is 20-30 min. Preferably, the vibration frequency in step (4) is 30-50 times/minute, and the vibration time is 2-6 minutes.
有益效果:Beneficial effect:
1、干燥养护时间短,可降低生产周期,有一定的经济性;1. The drying and curing time is short, which can reduce the production cycle and has certain economical efficiency;
2、飞灰使用率高,工艺利废率大,可极大程度实现废物再利用;2. The utilization rate of fly ash is high, and the waste rate of the process is large, which can realize the reuse of waste to a great extent;
3、产品可有效封闭飞灰中的重金属,同时有较好的蓄水、透水性能,具有一定的环境效益;3. The product can effectively seal heavy metals in fly ash, and at the same time has good water storage and water permeability performance, and has certain environmental benefits;
具体实施方式detailed description
实施例1:Example 1:
取100份高岭土置于坩埚中,置于700℃下的马弗炉中煅烧2h,待冷却至常温后,磨细过100目筛待用。取后生活垃圾焚烧飞灰70份、偏高岭土30份、氢氧化钠10份,置于容器中混匀,加30份水,以200转/分钟频率搅拌20min,混料搅拌后注入模具中以50次/分钟频率振实2min。模具置于80℃的干燥箱中干养护12h时间后拆模,拆模后的块件置于30℃的干燥箱中养护21天后得碱基地聚物生态材料。实施例1中试件的检测指标入下标所示。Take 100 parts of kaolin in a crucible, place it in a muffle furnace at 700°C for calcination for 2 hours, and after cooling to room temperature, grind it through a 100-mesh sieve for use. Take 70 parts of domestic waste incineration fly ash, 30 parts of metakaolin, and 10 parts of sodium hydroxide, put them in a container and mix them evenly, add 30 parts of water, stir at a frequency of 200 rpm for 20 minutes, pour the mixture into the mold to Vibrate at a frequency of 50 times/min for 2 minutes. The mold is placed in a drying oven at 80°C for 12 hours, and then the mold is removed, and the removed block is placed in a drying oven at 30°C for 21 days, and then the alkali-based polymer ecological material is obtained. The detection index of the test piece in embodiment 1 is shown in the subscript.
表1-1实施例1中的试件检测指标The test piece detection index in the table 1-1 embodiment 1
表1-2实施例1中的试件重金属浸出值The test piece heavy metal leaching value in the embodiment 1 of table 1-2
实施例2:Example 2:
取100份高岭土置于坩埚中,置于900℃下的马弗炉中煅烧0.5h,待冷却至常温后,磨细过100目筛待用。取生活垃圾焚烧飞灰61份、偏高岭土29份、硅酸钠20份置于容器中混匀,加22份水,以120转/分钟频率搅拌25min,混料搅拌后注入模具中以40次/分钟频率振实3min。模具置于50℃的干燥箱中干养护24h时间后拆模,拆模后的块件置于50℃的干燥箱中养护16天后得碱基地聚物生态材料。实施例2中试件的检测指标入下标所示。Take 100 parts of kaolin and place it in a crucible, place it in a muffle furnace at 900°C for calcination for 0.5h, and after cooling to room temperature, grind it through a 100-mesh sieve for use. Take 61 parts of household waste incineration fly ash, 29 parts of metakaolin, and 20 parts of sodium silicate in a container and mix them evenly, add 22 parts of water, stir at 120 rpm for 25 minutes, pour the mixture into the mold for 40 times Vibrate at a frequency of 3 minutes per minute. After the mold is placed in a drying oven at 50°C for 24 hours, the mold is removed, and the molded pieces are placed in a drying oven at 50°C for 16 days to obtain an alkaline-based polymer ecological material. The detection indexes of the test piece in embodiment 2 are shown in the subscript.
表2-1实施例2中的试件检测指标The test piece detection index in the table 2-1 embodiment 2
表2-2实施例2中的试件重金属浸出值The test piece heavy metal leaching value in the embodiment 2 of table 2-2
实施例3:Example 3:
取100份高岭土置于坩埚中,置于800℃下的马弗炉中煅烧1h,待冷却至常温后,磨细过100目筛待用。取生活垃圾焚烧飞灰50份、偏高岭土50份、氢氧化钾与硅酸钠各6份置于容器中混匀,加10份水,以50转/分钟频率搅拌30min,混料搅拌后注入模具中以20次/分钟频率振实6min。模具置于30℃的干燥箱中干养护48h时间后拆模,拆模后的块件置于80℃的干燥箱中养护12天后得碱基地聚物生态材料。实施例3中试件的检测指标入下标所示。Take 100 parts of kaolin and place it in a crucible, place it in a muffle furnace at 800°C for calcination for 1 hour, and after cooling to room temperature, grind it through a 100-mesh sieve for use. Take 50 parts of domestic waste incineration fly ash, 50 parts of metakaolin, 6 parts of potassium hydroxide and sodium silicate and mix them in a container, add 10 parts of water, stir at 50 rpm for 30 minutes, and inject the mixture after stirring Vibrate in the mold for 6 minutes at a frequency of 20 times/min. The mold was placed in a drying oven at 30°C for 48 hours and then removed, and the removed block was placed in a drying oven at 80°C for 12 days to obtain an alkaline-based polymer ecological material. The detection indexes of the test piece in embodiment 3 are shown in the subscript.
表3-1实施例3中的试件检测指标The test piece detection index in the table 3-1 embodiment 3
表3-2实施例3中的试件重金属浸出值The test piece heavy metal leaching value in the embodiment 3 in table 3-2
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