[go: up one dir, main page]

CN117263643A - Two-stage regulated full-solid waste micro-expansion concrete and preparation method thereof - Google Patents

Two-stage regulated full-solid waste micro-expansion concrete and preparation method thereof Download PDF

Info

Publication number
CN117263643A
CN117263643A CN202311549437.6A CN202311549437A CN117263643A CN 117263643 A CN117263643 A CN 117263643A CN 202311549437 A CN202311549437 A CN 202311549437A CN 117263643 A CN117263643 A CN 117263643A
Authority
CN
China
Prior art keywords
solid waste
gangue
parts
waste
carbide slag
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
CN202311549437.6A
Other languages
Chinese (zh)
Inventor
闫长旺
冯蓉蓉
张菊
白茹
王萧萧
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.)
Inner Mongolia University of Technology
Original Assignee
Inner Mongolia University of Technology
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 Inner Mongolia University of Technology filed Critical Inner Mongolia University of Technology
Priority to CN202311549437.6A priority Critical patent/CN117263643A/en
Publication of CN117263643A publication Critical patent/CN117263643A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B28/00Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
    • C04B28/14Compositions 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 calcium sulfate cements
    • C04B28/142Compositions 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 calcium sulfate cements containing synthetic or waste calcium sulfate cements
    • C04B28/144Compositions 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 calcium sulfate cements containing synthetic or waste calcium sulfate cements the synthetic calcium sulfate being a flue gas desulfurization product
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/00017Aspects relating to the protection of the environment

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Ceramic Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Organic Chemistry (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention discloses a two-stage regulated full-solid waste micro-expansion concrete and a preparation method thereof, wherein the concrete comprises the following components in parts by weight: 1072.67 parts of coarse aggregate, 585.09 parts of fine aggregate, 9.75-29.25 parts of expanding agent, 458.33-477.83 parts of cementing material and 219.41 parts of water; wherein, the coarse aggregate uses gangue, the fine aggregate uses waste ceramic, the cementing material uses solid waste-based cementing material, the expanding agent uses polylactic acid to wrap carbide slag micro-expanding agent, and the water uses laboratory tap water. The invention utilizes the solid waste to develop building materials and produce building materials, can effectively realize the reduction, harmlessness and recycling of the solid waste treatment, and has important significance for energy conservation, emission reduction and waste recycling of the solid waste. Coarse and fine aggregates, cementing materials, additives and the like required by the preparation of the concrete by utilizing the solid wastes can realize the comprehensive utilization of the solid wastes and promote the green development of the concrete industry.

Description

一种两阶段调控的全固废微膨胀混凝土及其制备方法A two-stage controlled all-solid waste micro-expanded concrete and its preparation method

技术领域Technical field

本发明具体涉及一种两阶段调控的全固废微膨胀混凝土及其制备方法。属于土木工程领域,属于固废资源化利用领域,属于建筑材料混凝土领域。The invention specifically relates to a two-stage controlled all-solid waste micro-expanded concrete and a preparation method thereof. It belongs to the field of civil engineering, the field of solid waste resource utilization, and the field of building materials concrete.

背景技术Background technique

在混凝土的硬化和使用过程中会产生体积收缩,过大的收缩可能导致结构开裂从而影响其性能。在配制混凝土时添加一定量的膨胀剂,使混凝土在硬化过程中产生体积膨胀,抵消收缩,从而防止结构开裂。目前常用氧化钙类膨胀剂存在膨胀速率过快,有效膨胀率较低等缺点,因此,仅利用膨胀剂来补偿混凝土的收缩形变难以满足实际生产需求。Volume shrinkage occurs during the hardening and use of concrete. Excessive shrinkage may cause cracks in the structure and affect its performance. When preparing concrete, a certain amount of expansion agent is added to cause the concrete to expand in volume during the hardening process and offset shrinkage, thus preventing structural cracking. Currently, calcium oxide expansion agents commonly used have shortcomings such as too fast expansion rate and low effective expansion rate. Therefore, it is difficult to meet actual production needs by only using expansion agents to compensate for the shrinkage deformation of concrete.

我国固体废弃物存量大、利用率低、存在较大的生态环境安全隐患。固废的建材化利用是解决其堆弃现状的主要途径之一。因此,利用固废制备粗、细骨料、水泥等材料,并将其应用于混凝土中制备全固废混凝土,提高固废的资源利用率,对于节约资源、推动混凝土行业绿色高质量发展具有重要意义。my country's solid waste stock is large, its utilization rate is low, and it poses great ecological and environmental safety risks. The utilization of solid waste as building materials is one of the main ways to solve the current situation of its disposal. Therefore, using solid waste to prepare coarse and fine aggregates, cement and other materials, and applying them to concrete to prepare all-solid waste concrete, improving the resource utilization rate of solid waste is important for saving resources and promoting the green and high-quality development of the concrete industry. significance.

专利CN102092976A,公开了一种生态大体积混凝土膨胀剂及制备方法,将菱镁矿尾矿和白云石尾矿配成生料,混合均匀,高温煅烧,在空气中冷却后,经过筛即得到生态大体积混凝土膨胀剂。发明利用CaO作为早期膨胀源,利用MgO作为后期膨胀源,可降低和补偿水工大体积混凝土的早期和后期收缩。但所述发明制备的膨胀剂存在氧化钙水化速度过快,混凝土后期膨胀率较低的缺点。Patent CN102092976A discloses an ecological large-volume concrete expansion agent and a preparation method. Magnesite tailings and dolomite tailings are prepared into raw materials, mixed evenly, calcined at high temperature, cooled in the air, and screened to obtain the ecological large-volume concrete expansion agent. Volumetric concrete expansion agent. The invention uses CaO as the early expansion source and MgO as the late expansion source, which can reduce and compensate for the early and late shrinkage of hydraulic mass concrete. However, the expansion agent prepared by the invention has the disadvantages of too fast hydration rate of calcium oxide and low later expansion rate of concrete.

专利CN 115180866 B,公开了一种水化热调节型镁质高效抗裂剂及其制备方法,包括以下质量百分数的各组分:膨胀组分50~80%、水化热调节组分1~5%、减缩组分1~5%、增强组分10~45%。发明能降低混凝土的温度收缩和自收缩,并且提高混凝土的力学性能。但发明所述膨胀组分属氧化镁类膨胀组分,早期膨胀率较低,无法补偿混凝土早期收缩。Patent CN 115180866 B discloses a hydration heat-adjusted magnesium high-efficiency anti-cracking agent and its preparation method, including the following components in mass percentage: expansion component 50-80%, hydration heat-adjusting component 1~ 5%, shrinkage reducing component 1~5%, strengthening component 10~45%. The invention can reduce the temperature shrinkage and autogenous shrinkage of concrete and improve the mechanical properties of concrete. However, the expansion component described in the invention is a magnesium oxide expansion component, which has a low early expansion rate and cannot compensate for the early shrinkage of concrete.

专利CN 116730680 A,公开了一种高抗裂性混凝土及其制备方法,原料包括水、粗集料、细集料、水、聚羧酸减水剂、钙镁复合膨胀剂、粉煤灰、橡胶粉改性多尺寸混合纤维材料、胶粘剂,发明具有较高强度和较好抗裂能力。专利CN 115304316 B,公开了一种补偿收缩型混凝土及其制备方法,原料包括:菱铁矿、石墨尾矿、水泥、减水剂、保水剂、粉煤灰、粗骨料、河砂和水。发明制备得到的混凝土抗压强度好,抗渗性强,密实度高。上述发明制备混凝土使用粉煤灰、菱铁矿、石墨尾矿等固体废弃物用作掺合料提高混凝土性能,但固废在混凝土中掺量较少,混凝土中固废利用率较低。Patent CN 116730680 A discloses a high crack-resistant concrete and its preparation method. The raw materials include water, coarse aggregate, fine aggregate, water, polycarboxylate water-reducing agent, calcium-magnesium composite expansion agent, fly ash, Rubber powder modified multi-size mixed fiber materials and adhesives are invented to have higher strength and better crack resistance. Patent CN 115304316 B discloses a shrinkage-compensating concrete and its preparation method. The raw materials include: siderite, graphite tailings, cement, water-reducing agent, water-retaining agent, fly ash, coarse aggregate, river sand and water . The concrete prepared by the invention has good compressive strength, strong impermeability and high density. The above invention uses solid waste such as fly ash, siderite, graphite tailings, etc. as admixtures to improve concrete performance, but the amount of solid waste in concrete is small, and the utilization rate of solid waste in concrete is low.

发明内容Contents of the invention

本发明的目的是克服现有的技术的不足,提供一种两阶段调控的全固废微膨胀混凝土及其制备方法。The purpose of the present invention is to overcome the shortcomings of the existing technology and provide a two-stage controlled all-solid waste micro-expanded concrete and a preparation method thereof.

混凝土的收缩形变会给工程带来安全隐患,使用膨胀剂可以补偿混凝土收缩带来的形变。其中,氧化镁类膨胀剂早期膨胀率较低,无法补偿混凝土的早期收缩,而氧化钙类膨胀剂与水反应迅速,往往氧化钙的水化反应在水泥硬化之前就已结束,因此造成混凝土的有效膨胀率低,无法补偿混凝土后期收缩变形。固体废弃物具有成分复杂、处理难度大、对环境污染严重等特点,利用固废开发建材和生产建材原料,可以有效实现固废处理的“减量化、无害化、资源化”,对于节能减排和将固废“变废为宝”具有重要意义。利用固废制备混凝土所需粗、细骨料、胶凝材料、外加剂等,可以实现固废的综合利用,推进混凝土产业绿色发展。The shrinkage deformation of concrete will bring safety hazards to the project. The use of expansion agents can compensate for the deformation caused by concrete shrinkage. Among them, the early expansion rate of magnesium oxide expansion agents is low and cannot compensate for the early shrinkage of concrete. However, calcium oxide expansion agents react quickly with water. The hydration reaction of calcium oxide often ends before the cement hardens, thus causing the concrete to shrink. The effective expansion rate is low and cannot compensate for the later shrinkage deformation of concrete. Solid waste has the characteristics of complex composition, difficult treatment, and serious environmental pollution. Using solid waste to develop building materials and produce building material raw materials can effectively achieve "reduction, harmlessness, and resource utilization" of solid waste treatment, which is beneficial to energy conservation. Emission reduction and turning solid waste into treasure are of great significance. Using solid waste to prepare coarse and fine aggregates, cementitious materials, admixtures, etc. required for concrete can achieve comprehensive utilization of solid waste and promote the green development of the concrete industry.

本发明采用的技术方案为:一种两阶段调控的全固废微膨胀混凝土,包括以下重量份的组分:粗骨料1072.67份、细骨料585.09份、膨胀剂9.75~29.25份、胶凝材料458.33~477.83份、水219.41份;其中,粗骨料使用煤矸石,细骨料使用废弃陶瓷,胶凝材料使用固废基胶凝材料,膨胀剂使用聚乳酸包裹电石渣微膨胀剂,水使用实验室自来水。The technical solution adopted by the present invention is: a two-stage controlled all-solid waste micro-expansion concrete, including the following components by weight: 1072.67 parts of coarse aggregate, 585.09 parts of fine aggregate, 9.75~29.25 parts of expansion agent, gelling agent 458.33~477.83 parts of material and 219.41 parts of water; among them, coal gangue is used as the coarse aggregate, waste ceramics are used as the fine aggregate, solid waste-based cementing material is used as the cementing material, polylactic acid-coated carbide slag micro-expansion agent is used as the expansion agent, and water Use laboratory tap water.

具体的,所述煤矸石取自内蒙古自治区鄂尔多斯市,煤矸石的化学组成为:SiO2为33.74%,Al2O3为31.67%,CaO为1.81%,SO3为1.59%,TiO2为1.21%,Fe2O3为0.74%,MgO为0.64%,其他氧化物为28.6%。煤矸石的堆积密度为1306kg/m3,表观密度为2659kg/m3,吸水率为5.32%。Specifically, the coal gangue was taken from Ordos City, Inner Mongolia Autonomous Region. The chemical composition of the coal gangue is: SiO 2 is 33.74%, Al 2 O 3 is 31.67%, CaO is 1.81%, SO 3 is 1.59%, and TiO 2 is 1.21 %, Fe 2 O 3 is 0.74%, MgO is 0.64%, and other oxides are 28.6%. The bulk density of coal gangue is 1306kg/m 3 , the apparent density is 2659kg/m 3 , and the water absorption rate is 5.32%.

具体的,所述废弃陶瓷取自景德镇市申达陶瓷厂生产过程中产生的废弃陶瓷。废弃陶瓷的表观密度为2460kg/m3。废弃陶瓷的化学组成包括:SiO2为67.82%,Al2O3为20.57%,K2O为3.87%,Fe2O3为2.32%,CaO为1.88%,Na2O为0.85%,SO3为0.82%,MgO为0.21%,其他氧化物为1.66%。废弃陶瓷细骨料的粒径分布为:0.08~0.16mm占比为13%,0.16~0.5mm占比为20%,0.5~1.0mm占比为34%,1.0~1.6mm占比为26%,1.6~2.0mm占比为7%。Specifically, the waste ceramics are obtained from the waste ceramics produced during the production process of Jingdezhen Shenda Ceramics Factory. The apparent density of waste ceramics is 2460kg/m 3 . The chemical composition of waste ceramics includes: SiO 2 is 67.82%, Al 2 O 3 is 20.57%, K 2 O is 3.87%, Fe 2 O 3 is 2.32%, CaO is 1.88%, Na 2 O is 0.85%, SO 3 It is 0.82%, MgO is 0.21%, and other oxides are 1.66%. The particle size distribution of waste ceramic fine aggregate is: 0.08~0.16mm accounts for 13%, 0.16~0.5mm accounts for 20%, 0.5~1.0mm accounts for 34%, and 1.0~1.6mm accounts for 26% , 1.6~2.0mm accounts for 7%.

具体的,所述固废基胶凝材料的化学组成为:SiO2为11.85%,Al2O3为18.44%,CaO为47.37%,SO3为14.93%,TiO2为0.45%,Fe2O3为1.41%,Na2O为1.98%,MgO为1.36%,其他氧化物为2.21%。Specifically, the chemical composition of the solid waste-based cementitious material is: SiO 2 is 11.85%, Al 2 O 3 is 18.44%, CaO is 47.37%, SO 3 is 14.93%, TiO 2 is 0.45%, Fe 2 O 3 is 1.41%, Na 2 O is 1.98%, MgO is 1.36%, and other oxides are 2.21%.

上述一种两阶段调控的全固废微膨胀混凝土的制备方法,包括以下步骤:The above-mentioned two-stage controlled preparation method of all-solid waste micro-expanded concrete includes the following steps:

步骤一:将煤矸石进行清洗、晾晒处理后,放入破碎机中进行破碎,筛分后得到粒径范围在5~20mm区间内的煤矸石粗骨料。Step 1: After cleaning and drying the gangue, put it into a crusher for crushing. After screening, coarse coal gangue aggregate with a particle size range of 5 to 20 mm is obtained.

步骤二:将废弃陶瓷进行清洗、晾晒处理,使用破碎机对废弃陶瓷进行破碎,使用粉碎机对废弃陶瓷进行研磨,使用振筛机对废弃陶瓷进行筛分处理,得到废弃陶瓷细骨料。Step 2: Clean and dry the waste ceramics, use a crusher to crush the waste ceramics, use a pulverizer to grind the waste ceramics, and use a vibrating screen machine to screen the waste ceramics to obtain waste ceramic fine aggregate.

步骤三:制备聚乳酸包裹电石渣微膨胀剂原料包括电石渣、聚乳酸、乙醇。聚乳酸主要成分是聚酯类聚合物。乙醇的沸点为78℃。电石渣的主要成分是氢氧化钙,电石渣在高温下煅烧生成氧化钙,发生化学反应:Ca(OH)2→CaO+H2O,其中,煅烧温度为800~900℃。Step 3: Prepare polylactic acid-coated carbide slag microexpansion agent raw materials including carbide slag, polylactic acid, and ethanol. The main component of polylactic acid is polyester polymer. The boiling point of ethanol is 78°C. The main component of calcium carbide slag is calcium hydroxide. Calcium carbide slag is calcined at high temperature to form calcium oxide, and a chemical reaction occurs: Ca(OH) 2 →CaO+H 2 O, where the calcination temperature is 800~900°C.

将电石渣在高温下煅烧得到氧化钙;将乙醇放入烧杯中,将聚乳酸在乙醇中进行溶解,聚乳酸和乙醇的质量比为0.8:1;将高温煅烧后的电石渣加入到聚乳酸/乙醇溶液中搅拌均匀,电石渣质量占比为60%~90%;将装有上述混合溶液的烧杯放入水浴锅中进行加热,其中,水浴温度85℃,加热时间为15min,在水浴锅中加热搅拌使乙醇蒸发,凝结成为固体;冷却至室温后对其进行破碎、粉磨,筛分,筛分粒径在150μm以上,制得聚乳酸包裹电石渣微膨胀剂。Calcide carbide slag at high temperature to obtain calcium oxide; put ethanol into a beaker, dissolve polylactic acid in ethanol, the mass ratio of polylactic acid and ethanol is 0.8:1; add calcium carbide slag calcined at high temperature to polylactic acid / ethanol solution, stir evenly, and the mass proportion of carbide slag is 60% to 90%; put the beaker containing the above mixed solution into a water bath for heating, where the water bath temperature is 85°C and the heating time is 15 minutes. The ethanol is heated and stirred to evaporate and condense into a solid; after cooling to room temperature, the ethanol is crushed, ground, and sieved to obtain a particle size of more than 150 μm to obtain a polylactic acid-coated carbide slag microexpansion agent.

步骤四:制备固废基胶凝材料的原材料包括以下重量份的组分:煤矸石30%、电石渣50%、脱硫石膏20%。煤矸石的化学组成为:SiO2为33.74%,Al2O3为31.67%,CaO为1.81%,SO3为1.59%,TiO2为1.21%,Fe2O3为0.74%,MgO为0.64%,其他氧化物为28.6%。电石渣的化学组成为:SiO2为7.62%,Al2O3为0.33%,CaO为67.26%,SO3为1.09%,TiO2为0.09%,Na2O为1.24%,其他氧化物为22.37%。脱硫石膏的化学组成为:SiO2为7.21%,Al2O3为0.31%,CaO为25.62%,SO3为47.62%,Na2O为3.91%,其他氧化物为15.33%。Step 4: The raw materials for preparing the solid waste-based cementitious material include the following components by weight: 30% coal gangue, 50% carbide slag, and 20% desulfurization gypsum. The chemical composition of coal gangue is: SiO 2 is 33.74%, Al 2 O 3 is 31.67%, CaO is 1.81%, SO 3 is 1.59%, TiO 2 is 1.21%, Fe 2 O 3 is 0.74%, MgO is 0.64% , other oxides are 28.6%. The chemical composition of carbide slag is: SiO 2 is 7.62%, Al 2 O 3 is 0.33%, CaO is 67.26%, SO 3 is 1.09%, TiO 2 is 0.09%, Na 2 O is 1.24%, and other oxides are 22.37 %. The chemical composition of desulfurization gypsum is: SiO 2 is 7.21%, Al 2 O 3 is 0.31%, CaO is 25.62%, SO 3 is 47.62%, Na 2 O is 3.91%, and other oxides are 15.33%.

将煤矸石进行清洗晾晒后放入破碎机进行破碎,用球磨机进行球磨,放入烘箱中以105℃烘干至恒重,取出后过200目方孔筛;同样将电石渣和脱硫石膏放入烘箱中,以105℃烘干至恒重,取出后过200目方孔筛;将煤矸石、电石渣和脱硫石膏按照配比称量,放入搅拌机中充分混合,之后加入原料总质量8%~10%的水搅拌均匀;将生料放入钢模具中压制成Ф6mm×5mm的小试饼,将试饼放入温度为105℃的鼓风干燥箱中烘干3h,使生料中的水分蒸发,使生料更易烧成;将生料放在高温箱式炉中进行煅烧,煅烧完成后立即取出试饼,冷却至室温;将试饼破碎成小块,用研磨机对其进行研磨,研磨时间设置为5min,研磨后过200目方孔筛;将二水石膏以质量比为5%与上述混合料混合均匀制得固废基胶凝材料。Clean and dry the coal gangue, put it into a crusher for crushing, grind it with a ball mill, dry it in an oven at 105°C to a constant weight, take it out and pass it through a 200-mesh square hole sieve; also put the carbide slag and desulfurization gypsum into In the oven, dry to constant weight at 105°C, take it out and pass it through a 200-mesh square hole sieve; weigh the coal gangue, carbide slag and desulfurization gypsum according to the proportions, put them into a mixer and mix them thoroughly, then add 8% of the total mass of the raw materials ~10% water and stir evenly; put the raw material into a steel mold and press it into a small test cake of Ф6mm×5mm. Put the test cake into a blast drying oven with a temperature of 105℃ and dry it for 3 hours to make the The water evaporates, making the raw material easier to burn; place the raw material in a high-temperature box furnace for calcination. Immediately after the calcination is completed, take out the test cake and cool it to room temperature; break the test cake into small pieces and grind it with a grinder , the grinding time is set to 5 minutes, and after grinding, pass through a 200-mesh square hole sieve; mix the dihydrate gypsum with the above mixture at a mass ratio of 5% to obtain a solid waste-based cementitious material.

具体的,所述步骤四中煅烧制度为:室温到950℃,升温速率设置为10℃/min,目的是去除生料中的结晶水;950℃到1290℃时,升温速率设置为5℃/min,升温速率降低的目的是生料球能够充分发生反应;升温到1290℃时,保温45min。高温煅烧过程中,原料中的氧化钙、氧化硅和硫酸钙发生化学反应生成硫铝酸钙,反应方程式为:3CaO+3Al2O3+CaSO4→C4A3S。Specifically, the calcination system in step 4 is: from room temperature to 950°C, the heating rate is set to 10°C/min, with the purpose of removing crystal water in the raw material; when 950°C to 1290°C, the heating rate is set to 5°C/min. min, the purpose of reducing the heating rate is to allow the raw material balls to fully react; when the temperature reaches 1290°C, keep it warm for 45 minutes. During the high-temperature calcination process, calcium oxide, silicon oxide and calcium sulfate in the raw materials react chemically to form calcium sulfoaluminate. The reaction equation is: 3CaO+3Al 2 O 3 +CaSO 4 →C 4 A 3 S.

本发明全固废微膨胀混凝土的微膨胀性能通过两阶段进行调控,第一阶段膨胀由聚乳酸包裹电石渣微膨胀剂提供,第二阶段膨胀由固废基胶凝材料提供,两阶段调控全固废微膨胀混凝土调控机理如下:The micro-expansion performance of the all-solid waste micro-expansion concrete of the present invention is regulated in two stages. The first-stage expansion is provided by the polylactic acid-coated carbide slag micro-expansion agent, and the second-stage expansion is provided by the solid waste-based cementitious material. The two-stage regulation is fully The control mechanism of solid waste micro-expansion concrete is as follows:

(1)混凝土第一阶段的膨胀主要由上述制备的聚乳酸包裹电石渣微膨胀剂进行提供,电石渣高温煅烧生成氧化钙,氧化钙水化生成氢氧化钙,在固相体积增大的同时,水化产物局部堆积导致孔隙体积增大,从而引起混凝土中浆体的体积膨胀。由于氧化钙遇水即发生放热反应,会导致水化速率快,有效膨胀率低等缺点,聚乳酸包裹电石渣微膨胀剂可以延缓水化时间,降低反应速率,提高混凝土的有效膨胀率。其中,氧化钙的水化反应方程式为:CaO+H2O→Ca(OH)2(1) The expansion of concrete in the first stage is mainly provided by the polylactic acid-coated carbide slag micro-expansion agent prepared above. The carbide slag is calcined at high temperature to generate calcium oxide, and the calcium oxide is hydrated to generate calcium hydroxide. While the solid phase volume increases, , the local accumulation of hydration products leads to an increase in pore volume, thereby causing the volume expansion of the slurry in concrete. Since calcium oxide undergoes an exothermic reaction when it meets water, it will lead to shortcomings such as fast hydration rate and low effective expansion rate. Polylactic acid-coated carbide slag micro-expansion agent can delay the hydration time, reduce the reaction rate, and increase the effective expansion rate of concrete. Among them, the hydration reaction equation of calcium oxide is: CaO+H 2 O → Ca(OH) 2 .

(2)混凝土第二阶段的膨胀主要由固废基胶凝材料进行提供,固废基胶凝材料的主要成分是硫铝酸钙(C4A3S)、硫酸钙(CaSO4),C4A3S和CaSO4与水发生水化反应生成钙矾石(C3A3·CS·32H)和铝凝胶(AH3),反应方程式为:C4A3S+2CS+38H→C3A3·CS·32H+2AH3,钙矾石晶体的生长,导致混凝土的膨胀。随水化反应的进行,CaSO4被消耗,硫铝酸钙发生水化反应生成单硫型水化硫铝酸钙(C3A·CS·12H),反应方程式为:C4A3S+18H→C3A·CS·12H+4AH3,生成的单硫型水化硫铝酸钙晶体,同样可以为混凝土提供后期膨胀。随水化反应的进行,固废基胶凝材料水化反应生成钙矾石和单硫型水化硫铝酸钙晶体,为混凝土提供第二阶段膨胀。(2) The second stage of concrete expansion is mainly provided by solid waste-based cementitious materials. The main components of solid waste-based cementitious materials are calcium sulfoaluminate (C 4 A 3 S), calcium sulfate (CaSO 4 ), C 4 A 3 S and CaSO 4 react with water to form ettringite (C 3 A 3 ·CS ·32H) and aluminum gel (AH 3 ). The reaction equation is: C 4 A 3 S+2CS+38H→ C 3 A 3 ·CS·32H+2AH 3 , the growth of ettringite crystals leads to the expansion of concrete. As the hydration reaction proceeds, CaSO 4 is consumed, and calcium sulfoaluminate undergoes a hydration reaction to generate monosulfide hydrated calcium sulfoaluminate (C 3 A·CS·12H). The reaction equation is: C 4 A 3 S+ 18H→C 3 A·CS·12H+4AH 3 , the monosulfur type calcium sulfoaluminate hydrate crystal generated can also provide late expansion for concrete. As the hydration reaction proceeds, the hydration reaction of the solid waste-based cementitious material generates ettringite and monosulfur-type calcium sulfoaluminate hydrate crystals, which provide the second stage of expansion for the concrete.

本发明的有益效果:Beneficial effects of the present invention:

1、使用煤矸石、电石渣、脱硫石膏、废弃陶瓷等固体废弃物制备全固废混凝土,可以大规模消纳固废,减少环境污染。1. Use coal gangue, calcium carbide slag, desulfurization gypsum, waste ceramics and other solid waste to prepare all-solid waste concrete, which can consume solid waste on a large scale and reduce environmental pollution.

2、使用聚乳酸和电石渣为原材料制备的聚乳酸包裹电石渣微膨胀剂,可以为混凝土提供第一阶段膨胀,氧化钙与水发生化学反应生成氢氧化钙,固相体积增大导致混凝土膨胀。由于氧化钙与水反应迅速,水化速率过快,使用聚乳酸对氧化钙进行包裹,可以有效延缓水化进程,提高混凝土的有效膨胀率。2. The polylactic acid-coated calcium carbide slag micro-expansion agent prepared using polylactic acid and carbide slag as raw materials can provide the first stage of expansion for concrete. Calcium oxide reacts chemically with water to generate calcium hydroxide. The increase in solid phase volume causes the concrete to expand. . Since calcium oxide reacts quickly with water and the hydration rate is too fast, using polylactic acid to wrap calcium oxide can effectively delay the hydration process and increase the effective expansion rate of concrete.

3、使用煤矸石、电石渣、脱硫石膏为原材料制备固废基胶凝材料,可以为混凝土提供第二阶段膨胀,固废基胶凝材料主要成分是硫铝酸钙(C4A3S)、硫酸钙(CaSO4),其中,C4A3S和CaSO4与水发生水化反应生成钙矾石(C3A3·CS·32H),C4A3S与水发生水化反应生成单硫型水化硫铝酸钙(C3A·CS·12H)。随水化反应的进行,固废基胶凝材料水化反应生成钙矾石和单硫型水化硫铝酸钙晶体,为混凝土提供第二阶段膨胀。3. Use coal gangue, calcium carbide slag, and desulfurization gypsum as raw materials to prepare solid waste-based cementitious materials, which can provide the second stage of expansion for concrete. The main component of solid waste-based cementitious materials is calcium sulfoaluminate (C 4 A 3 S) , calcium sulfate (CaSO 4 ), among which, C 4 A 3 S and CaSO 4 react with water to form ettringite (C 3 A 3 · CS · 32H), and C 4 A 3 S reacts with water to form ettringite. Generates monosulfide calcium sulfoaluminate hydrate (C 3 A·CS·12H). As the hydration reaction proceeds, the hydration reaction of the solid waste-based cementitious material generates ettringite and monosulfur-type calcium sulfoaluminate hydrate crystals, which provide the second stage of expansion for the concrete.

4、本发明提供一种两阶段调控的全固废微膨胀混凝土及其制备方法,两阶段调控方法可以有效提高混凝土膨胀率,补偿混凝土由于收缩带来的形变。4. The present invention provides a two-stage controlled all-solid waste micro-expansion concrete and a preparation method thereof. The two-stage control method can effectively increase the expansion rate of concrete and compensate for the deformation of concrete due to shrinkage.

具体实施方式Detailed ways

下面结合具体实施方式对本发明做进一步描述。The present invention will be further described below in conjunction with specific embodiments.

根据《普通混凝土设计规程》(JGJ 55-2011)以及《混凝土膨胀剂》(GB/T 23439-2017)对混凝土进行配合比设计,配合比设计表如下:The mix proportion design of concrete is carried out according to the "Design Regulations for Ordinary Concrete" (JGJ 55-2011) and "Concrete Expansion Agent" (GB/T 23439-2017). The mix proportion design table is as follows:

表1 配合比设计Table 1 Mix proportion design

其中,粗骨料使用煤矸石,细骨料使用废弃陶瓷,胶凝材料使用固废基胶凝材料,膨胀剂使用聚乳酸包裹电石渣微膨胀剂,水使用实验室自来水。Among them, coal gangue is used as the coarse aggregate, waste ceramics are used as the fine aggregate, solid waste-based cementing material is used as the cementing material, polylactic acid-coated carbide slag micro-expansion agent is used as the expansion agent, and laboratory tap water is used as the water.

实施例1Example 1

本发明提供一种两阶段调控的全固废微膨胀混凝土及其制备方法,包括以下重量份的组分:煤矸石粗骨料1072.67份、废弃陶瓷细骨料585.09份、聚乳酸包裹电石渣微膨胀剂9.75份、固废基胶凝材料477.83份、水219.41份。The invention provides a two-stage controlled all-solid waste micro-expanded concrete and a preparation method thereof, which includes the following components by weight: 1072.67 parts of coal gangue coarse aggregate, 585.09 parts of waste ceramic fine aggregate, polylactic acid-coated carbide slag micro-aggregate 9.75 parts of expansion agent, 477.83 parts of solid waste-based cementitious material, and 219.41 parts of water.

实施例2Example 2

本发明提供一种两阶段调控的全固废微膨胀混凝土及其制备方法,包括以下重量份的组分:煤矸石粗骨料1072.67份、废弃陶瓷细骨料585.09份、聚乳酸包裹电石渣微膨胀剂14.6份、固废基胶凝材料472.98份、水219.41份。The invention provides a two-stage controlled all-solid waste micro-expanded concrete and a preparation method thereof, which includes the following components by weight: 1072.67 parts of coal gangue coarse aggregate, 585.09 parts of waste ceramic fine aggregate, polylactic acid-coated carbide slag micro-aggregate 14.6 parts of expansion agent, 472.98 parts of solid waste-based cementitious material, and 219.41 parts of water.

实施例3Example 3

本发明提供一种两阶段调控的全固废微膨胀混凝土及其制备方法,包括以下重量份的组分:煤矸石粗骨料1072.67份、废弃陶瓷细骨料585.09份、聚乳酸包裹电石渣微膨胀剂19.5份、固废基胶凝材料468.08份、水219.41份。The invention provides a two-stage controlled all-solid waste micro-expanded concrete and a preparation method thereof, which includes the following components by weight: 1072.67 parts of coal gangue coarse aggregate, 585.09 parts of waste ceramic fine aggregate, polylactic acid-coated carbide slag micro-aggregate 19.5 parts of expansion agent, 468.08 parts of solid waste-based cementitious material, and 219.41 parts of water.

实施例4Example 4

本发明提供一种两阶段调控的全固废微膨胀混凝土及其制备方法,包括以下重量份的组分:煤矸石粗骨料1072.67份、废弃陶瓷细骨料585.09份、聚乳酸包裹电石渣微膨胀剂24.4份、固废基胶凝材料463.18份、水219.41份。The invention provides a two-stage controlled all-solid waste micro-expanded concrete and a preparation method thereof, which includes the following components by weight: 1072.67 parts of coal gangue coarse aggregate, 585.09 parts of waste ceramic fine aggregate, polylactic acid-coated carbide slag micro-aggregate There are 24.4 parts of expansion agent, 463.18 parts of solid waste-based cementitious material, and 219.41 parts of water.

实施例5Example 5

本发明提供一种两阶段调控的全固废微膨胀混凝土及其制备方法,包括以下重量份的组分:煤矸石粗骨料1072.67份、废弃陶瓷细骨料585.09份、聚乳酸包裹电石渣微膨胀剂0份、固废基胶凝材料458.33份、水219.41份。The invention provides a two-stage controlled all-solid waste micro-expanded concrete and a preparation method thereof, which includes the following components by weight: 1072.67 parts of coal gangue coarse aggregate, 585.09 parts of waste ceramic fine aggregate, polylactic acid-coated carbide slag micro-aggregate 0 parts of expansion agent, 458.33 parts of solid waste-based cementitious material, and 219.41 parts of water.

对比例1Comparative example 1

本发明提供一种两阶段调控的全固废微膨胀混凝土及其制备方法,包括以下重量份的组分:煤矸石粗骨料1072.67份、废弃陶瓷细骨料585.09份、聚乳酸包裹电石渣微膨胀剂0份、固废基胶凝材料487.58份、水219.41份。The invention provides a two-stage controlled all-solid waste micro-expanded concrete and a preparation method thereof, which includes the following components by weight: 1072.67 parts of coal gangue coarse aggregate, 585.09 parts of waste ceramic fine aggregate, polylactic acid-coated carbide slag micro-aggregate 0 parts of expansion agent, 487.58 parts of solid waste-based gelling material, and 219.41 parts of water.

根据《混凝土长期性能和耐久性试验方法标准》(GB/T 50082-2009)对混凝土微应变进行测试。测得一种两阶段调控的全固废微膨胀混凝土的微应变结果如下:The concrete microstrain was tested according to the "Standard for Test Methods of Long-term Performance and Durability of Concrete" (GB/T 50082-2009). The measured micro-strain results of a two-stage controlled all-solid waste micro-expanded concrete are as follows:

表2 混凝土微应变/μεTable 2 Concrete microstrain/με

结果表明:(1)根据实施例1~实施例5可知,随聚乳酸包裹电石渣微膨胀剂掺量的增加,全固废混凝土的微应变逐渐增加,且早期微应变增长速率加快,说明微膨胀剂的早期膨胀效果好,为混凝土提供第一阶段膨胀。(2)根据实施例1~5和对比例1可知,不掺膨胀剂的情况下,混凝土的微应变随龄期逐渐增加,说明固废基胶凝材料可以作为全固废混凝土的膨胀源,为混凝土提供第二阶段膨胀。The results show: (1) According to Examples 1 to 5, with the increase in the amount of polylactic acid-coated carbide slag microexpansion agent, the microstrain of the solid waste concrete gradually increases, and the early microstrain growth rate accelerates, indicating that the microstrain The early expansion effect of the expansion agent is good, providing the first stage of expansion for the concrete. (2) According to Examples 1 to 5 and Comparative Example 1, it can be seen that without the addition of expansion agent, the microstrain of concrete gradually increases with age, indicating that solid waste-based cementitious materials can be used as the expansion source of fully solid waste concrete. Provides a second stage of expansion for concrete.

应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明原理的前提下,还可以做出若干改进和润饰,这些改进和润饰也应视为本发明的保护范围。本实施例中未明确的各组成部分均可用现有技术加以实现。It should be pointed out that for those of ordinary skill in the art, several improvements and modifications can be made without departing from the principles of the present invention, and these improvements and modifications should also be regarded as the protection scope of the present invention. All components not specified in this embodiment can be implemented using existing technologies.

Claims (6)

1. A two-stage regulated full-solid waste micro-expansion concrete is characterized in that: comprises the following components in parts by weight: 1072.67 parts of coarse aggregate, 585.09 parts of fine aggregate, 9.75-29.25 parts of expanding agent, 458.33-477.83 parts of cementing material and 219.41 parts of water; wherein, the coarse aggregate uses gangue, the fine aggregate uses waste ceramic, the cementing material uses solid waste-based cementing material, the expanding agent uses polylactic acid to wrap carbide slag micro-expanding agent, and the water uses laboratory tap water.
2. The two-stage regulated total solid waste micro-expansive concrete according to claim 1, wherein: the chemical composition of the gangue is as follows: siO (SiO) 2 33.74% of Al 2 O 3 31.67%, caO 1.81%, SO 3 1.59% TiO 2 1.21% of Fe 2 O 3 0.74%, mgO 0.64%, other oxides 28.6%; the bulk density of the gangue is 1306kg/m 3 Apparent density of 2659kg/m 3 The water absorption was 5.32%.
3. The two-stage regulated total solid waste micro-expansive concrete according to claim 2, wherein: the apparent density of the waste ceramic is 2460kg/m 3 The method comprises the steps of carrying out a first treatment on the surface of the The chemical composition of the waste ceramic comprises: siO (SiO) 2 67.82, al 2 O 3 20.57%, K 2 O is 3.87%, fe 2 O 3 2.32%, caO 1.88%, na 2 O is 0.85%, SO 3 0.82%, mgO 0.21%, other oxides 1.66%; the particle size distribution of the waste ceramic fine aggregate is as follows: 13% of 0.08-0.16 mm, 20% of 0.16-0.5 mm, 34% of 0.5-1.0 mm, 26% of 1.0-1.6 mm and 7% of 1.6-2.0 mm.
4. A two-stage controlled all-solid-waste micro-expansive concrete according to claim 3, characterized in that: the solid waste-based cementing material comprises the following chemical components: siO (SiO) 2 11.85% of Al 2 O 3 18.44%, caO 47.37%, SO 3 14.93% TiO 2 0.45% of Fe 2 O 3 1.41% of Na 2 O is 1.98%, mgO is 1.36%, and other oxides are 2.21%.
5. The method for preparing the two-stage regulated full-solid waste micro-expansive concrete according to claim 1, 2, 3 or 4, which is characterized by comprising the following steps: the method comprises the following steps:
step one: washing and airing the gangue, putting the gangue into a crusher for crushing, and screening to obtain gangue coarse aggregate with the particle size within a range of 5-20 mm;
step two: cleaning and airing the waste ceramics, crushing the waste ceramics by using a crusher, grinding the waste ceramics by using a crusher, and screening the waste ceramics by using a vibrating screen to obtain waste ceramic fine aggregate;
step three: the polylactic acid coated carbide slag micro-expanding agent is prepared from carbide slag, polylactic acid and ethanol; the polylactic acid is mainly composed of polyester polymers; the boiling point of ethanol is 78 ℃; main component of carbide slagCalcium hydroxide is adopted, calcium oxide is generated by calcining carbide slag at high temperature, and chemical reaction is carried out: ca (OH) 2 →CaO+H 2 O, wherein the calcination temperature is 800-900 ℃;
calcining carbide slag at high temperature to obtain calcium oxide; putting ethanol into a beaker, dissolving polylactic acid in the ethanol, wherein the mass ratio of the polylactic acid to the ethanol is 0.8:1; adding the carbide slag subjected to high-temperature calcination into polylactic acid/ethanol solution, and uniformly stirring, wherein the mass ratio of the carbide slag is 60% -90%; heating the beaker filled with the mixed solution in a water bath kettle for 15min at the water bath temperature of 85 ℃, heating and stirring in the water bath kettle to evaporate ethanol and coagulate into solid; cooling to room temperature, crushing, grinding, sieving to obtain polylactic acid coated carbide slag micro-expanding agent with particle size over 150 μm;
step four: the raw materials for preparing the solid waste-based cementing material comprise the following components in parts by weight: 30% of gangue, 50% of carbide slag and 20% of desulfurized gypsum; the chemical composition of the gangue is as follows: siO (SiO) 2 33.74% of Al 2 O 3 31.67%, caO 1.81%, SO 3 1.59% TiO 2 1.21% of Fe 2 O 3 0.74%, mgO 0.64%, other oxides 28.6%; the chemical composition of the carbide slag is as follows: siO (SiO) 2 7.62% of Al 2 O 3 0.33%, 67.26% CaO and SO 3 1.09%, tiO 2 0.09%, na 2 O1.24% and other oxides 22.37%; the chemical composition of the desulfurized gypsum is as follows: siO (SiO) 2 7.21% of Al 2 O 3 0.31%, 25.62% CaO and SO 3 47.62, na 2 O3.91% and other oxides 15.33%;
washing and airing gangue, putting the gangue into a crusher for crushing, ball-milling the gangue by using a ball mill, putting the gangue into an oven for drying at 105 ℃ until the gangue is constant in weight, taking the gangue out, and sieving the gangue with a 200-mesh square-hole sieve; placing carbide slag and desulfurized gypsum into an oven, drying at 105 ℃ to constant weight, taking out, and sieving with a 200-mesh square-hole sieve; weighing coal gangue, carbide slag and desulfurized gypsum according to a proportion, putting the mixture into a stirrer for fully mixing, and then adding water accounting for 8% -10% of the total mass of the raw materials for uniformly stirring; placing the raw material into a steel mould to be pressed into small test cakes with the diameter of phi 6mm multiplied by 5mm, placing the test cakes into a blast drying oven with the temperature of 105 ℃ to be dried for 3 hours, and evaporating the water in the raw material to enable the raw material to be easier to be sintered; placing the raw materials in a high-temperature box-type furnace for calcination, immediately taking out the test cakes after the calcination is completed, and cooling to room temperature; crushing the test cake into small blocks, grinding the small blocks by a grinder, setting the grinding time to be 5min, and sieving the small blocks by a 200-mesh square hole sieve after grinding; and uniformly mixing the dihydrate gypsum with the mixture in a mass ratio of 5% to prepare the solid waste base cementing material.
6. The preparation method of the two-stage regulated full-solid waste micro-expansive concrete is characterized by comprising the following steps of: the calcination system in the fourth step is as follows: the temperature is set to be 10 ℃ per minute from room temperature to 950 ℃, and the purpose is to remove the crystal water in the raw material; setting the heating rate to be 5 ℃/min at 950 ℃ to 1290 ℃, wherein the purpose of reducing the heating rate is that raw material balls can fully react; heating to 1290 ℃, and preserving heat for 45min; in the high-temperature calcination process, calcium oxide, silicon oxide and calcium sulfate in the raw materials react chemically to generate calcium sulfoaluminate.
CN202311549437.6A 2023-11-21 2023-11-21 Two-stage regulated full-solid waste micro-expansion concrete and preparation method thereof Pending CN117263643A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202311549437.6A CN117263643A (en) 2023-11-21 2023-11-21 Two-stage regulated full-solid waste micro-expansion concrete and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202311549437.6A CN117263643A (en) 2023-11-21 2023-11-21 Two-stage regulated full-solid waste micro-expansion concrete and preparation method thereof

Publications (1)

Publication Number Publication Date
CN117263643A true CN117263643A (en) 2023-12-22

Family

ID=89210848

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202311549437.6A Pending CN117263643A (en) 2023-11-21 2023-11-21 Two-stage regulated full-solid waste micro-expansion concrete and preparation method thereof

Country Status (1)

Country Link
CN (1) CN117263643A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN119038912A (en) * 2024-10-30 2024-11-29 内蒙古工业大学 Full-solid waste micro-expansion concrete and preparation method thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109553355A (en) * 2018-12-26 2019-04-02 成都宏基建材股份有限公司 A kind of C40P12 subway concrete and preparation method thereof
CN109704676A (en) * 2019-01-19 2019-05-03 江苏盛达飞建筑材料有限公司 A kind of impervious regeneration concrete and preparation method thereof
CN112939508A (en) * 2021-02-19 2021-06-11 内蒙古工业大学 Carbide slag-based micro-expanding agent and preparation method thereof
CN116675509A (en) * 2023-06-20 2023-09-01 内蒙古工业大学 A kind of all-solid-waste steam-free concrete and its application

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109553355A (en) * 2018-12-26 2019-04-02 成都宏基建材股份有限公司 A kind of C40P12 subway concrete and preparation method thereof
CN109704676A (en) * 2019-01-19 2019-05-03 江苏盛达飞建筑材料有限公司 A kind of impervious regeneration concrete and preparation method thereof
CN112939508A (en) * 2021-02-19 2021-06-11 内蒙古工业大学 Carbide slag-based micro-expanding agent and preparation method thereof
CN116675509A (en) * 2023-06-20 2023-09-01 内蒙古工业大学 A kind of all-solid-waste steam-free concrete and its application

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN119038912A (en) * 2024-10-30 2024-11-29 内蒙古工业大学 Full-solid waste micro-expansion concrete and preparation method thereof
CN119038912B (en) * 2024-10-30 2025-02-11 内蒙古工业大学 Full-solid waste micro-expansion concrete and preparation method thereof

Similar Documents

Publication Publication Date Title
Chindaprasirt et al. Utilization of blended fluidized bed combustion (FBC) ash and pulverized coal combustion (PCC) fly ash in geopolymer
CN108358581B (en) A kind of concrete containing refining slag and preparation method thereof
CN103964713B (en) Flyash and Bayer process red mud is utilized to prepare the method for belite aluminosulfate cement
CN104529319B (en) Low-heat micro-expansion composite cement and preparation method thereof
CN108483953A (en) A kind of low hydration heat copper ashes base composite gelled material and preparation method thereof
CN109942238A (en) A kind of preparation method of quick setting quick hard coal gangue alkali excited quick repair material
CN108821671A (en) A kind of full Industrial Solid Waste high intensity instant foam concrete material and preparation method
CN102718423A (en) Preparation method of low-grade activated coal ash composite material
CN114605121B (en) A kind of tungsten tailings autoclaved aerated concrete and its preparation method
CN103319103A (en) Regenerative hardened cement mortar gelling material and preparation method thereof
CN112794683B (en) A kind of waste concrete-based recycled cementitious material and preparation method thereof
CN116675509A (en) A kind of all-solid-waste steam-free concrete and its application
CN105198324A (en) Self-compacting concrete containing bayer-process red mud and preparation method thereof
CN117263643A (en) Two-stage regulated full-solid waste micro-expansion concrete and preparation method thereof
CN105693125B (en) A kind of sulphate aluminium cement heat stabilizer and its application method
CN103145362A (en) Method for preparing cement concrete early strength agent by using industrial residue
CN111268988A (en) High-water-resistance calcination-free phosphogypsum-based slope building block material and preparation thereof
CN114890765A (en) Plastering gypsum and preparation method thereof
CN109336428B (en) Preparation method of layered cement and MSWI bottom ash-alkali stimulated double cementation system
CN101215110B (en) Treatment method of comprehensive utilization of air-entrained concrete waste
CN114956642B (en) Composite expanding agent based on regenerated micro powder and preparation method thereof
CN117623655A (en) Geopolymer precursor powder convenient for on-site construction and its preparation method and construction method
CN114477810B (en) A low-carbon, low-heat, high-belite cement clinker based on waste concrete and its preparation method
CN116835893A (en) A kind of retarded expansion cement compounded with multiple solid wastes and its preparation method
CN115710095A (en) Boron-phosphorus composite modified high belite sulphoaluminate cement clinker and preparation method 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