CN114591013B - Artificial aggregate of river sludge and preparation method thereof - Google Patents
Artificial aggregate of river sludge and preparation method thereof Download PDFInfo
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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
- C04B18/00—Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
- C04B18/02—Agglomerated materials, e.g. artificial aggregates
- C04B18/021—Agglomerated materials, e.g. artificial aggregates agglomerated by a mineral binder, e.g. cement
-
- 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
- C04B20/00—Use of materials as fillers for mortars, concrete or artificial stone according to more than one of groups C04B14/00 - C04B18/00 and characterised by shape or grain distribution; Treatment of materials according to more than one of the groups C04B14/00 - C04B18/00 specially adapted to enhance their filling properties in mortars, concrete or artificial stone; Expanding or defibrillating materials
- C04B20/10—Coating or impregnating
- C04B20/1055—Coating or impregnating with inorganic materials
- C04B20/1074—Silicates, e.g. glass
-
- 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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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Ceramic Engineering (AREA)
- Materials Engineering (AREA)
- Structural Engineering (AREA)
- Organic Chemistry (AREA)
- Civil Engineering (AREA)
- Inorganic Chemistry (AREA)
- Curing Cements, Concrete, And Artificial Stone (AREA)
Abstract
Description
技术领域technical field
本发明涉及一种利用河道淤泥作为主要原料采用挤出成型法制备免烧结人造集料的方法,属于轻结构混凝土用人造集料领域。The invention relates to a method for preparing sinter-free artificial aggregate by using river silt as a main raw material by extrusion molding, and belongs to the field of artificial aggregate for light-structure concrete.
背景技术Background technique
长江流域河道淤泥是一种在长江流域河段内尤其是中下游地段内大量淤积的无法固结的细软颗粒。其成分极其复杂包括无机非矿,生物残体,有机沉淀和含铁镁胶体等十多余种成分。作为一种常见的固体垃圾,河道污泥的淤积具有多种危害,以长三角地区为例,这些污泥往往导致水体黑臭,严重影响当地渔业和农业发展,此外它们还会抬高河床位置,使得汛期危险系数提高,甚至在关键地形淤积,影响大型船只正常通航,大大折损江南水网的航运价值。为了应对这一严峻问题,各级政府在国家战略的号召下多次组织开展清淤工程项目,这些项目每年产生数以千万吨的淤泥带来严重的环境压力。以长江流域下游的太湖为例,太湖总面积超过2500km3,平均淤积深度超过0.5m,仅2007政府发布《太湖水污染治理方案》一个项目就产生3000万m3淤泥。The river silt in the Yangtze River Basin is a kind of unconsolidated fine and soft particles that accumulate in large quantities in the Yangtze River Basin, especially in the middle and lower reaches. Its composition is extremely complex, including inorganic non-minerals, biological residues, organic precipitates and iron-magnesium colloids and more than ten kinds of components. As a common solid waste, the sedimentation of river sludge has many hazards. Taking the Yangtze River Delta region as an example, these sludges often lead to black and odorous water bodies, which seriously affects the development of local fisheries and agriculture. In addition, they also raise the position of the riverbed. , which increases the risk factor during the flood season, and even accumulates in key terrain, which affects the normal navigation of large ships and greatly reduces the shipping value of the Jiangnan water network. In order to deal with this serious problem, governments at all levels have organized and carried out dredging projects under the call of the national strategy for many times. These projects produce tens of millions of tons of silt every year and bring serious environmental pressure. Taking Taihu Lake in the lower reaches of the Yangtze River Basin as an example, the total area of Taihu Lake exceeds 2500km 3 , and the average deposition depth exceeds 0.5m. In 2007, the government issued the “Taihu Lake Water Pollution Control Plan” alone, which produced 30 million m 3 of silt.
面对堆积如山的开挖河道淤泥,如何更好的处置成为了一个迫在眉睫的问题。常用的方法包括填埋堆放、农业利用或者作为建筑原料等都存在很大的局限性,如直接填埋堆放占地面积过大,极其容易造成二次污染;用做农田肥料或者湿地回填,淤泥的需求量太少,处理周期太长;作为建筑原料,目前的烧结墙体砖或者烧胀集料能耗较高,不符合国家节能战略。因此,我们亟需一种更加值得推广的淤泥资源化利用方式来解决目前大量产生的河道淤泥给环境带来的巨大压力。In the face of the mountains of excavated river silt, how to better dispose of it has become an urgent problem. Commonly used methods include landfilling, agricultural utilization or as building materials, etc., all have great limitations. For example, direct landfilling covers an excessively large area, which is extremely likely to cause secondary pollution; used as farmland fertilizer or wetland backfill, silt The demand is too small, and the processing cycle is too long; as building materials, the current sintered wall bricks or swelled aggregates have high energy consumption, which does not conform to the national energy-saving strategy. Therefore, we urgently need a more worthy of promotion of silt resource utilization to solve the huge pressure on the environment caused by the current mass production of river silt.
近年来,新型建筑材料技术的提出为河道淤泥的高效资源化利用带来的崭新的解决思路。大量前期研究表明,脱水处理后的河道淤泥的矿物成分与风化产生的粘土有诸多相似之处。河道淤泥的产生是河流上游山体矿物风化、地表沙石风化细颗粒随雨水冲刷在下游沉积,或者河床中的岩石沙砾长期被水流冲刷侵蚀的结果,该过程的产物本质为粘土,因此河道淤泥在制备新型建筑材料方面具有极高的利用价值。粘土类矿物本身具有的特性也使得其原料塑性指数大,粘结性好,适合工业造粒成球。目前大量的相关研究主要集中于利用河道淤泥制备新型墙体烧结砖,或者代替页岩等制备烧结集料等,这些方法都能在一定程度上解决淤泥利用问题,但其能耗过高、尾气排放污染严重等问题限制了产品推广应用。In recent years, the introduction of new building material technology has brought new solutions to the efficient resource utilization of river silt. A large number of previous studies have shown that the mineral composition of dewatered river silt has many similarities with the clay produced by weathering. The generation of river silt is the result of the weathering of minerals in the upper reaches of the river, the weathering of surface sand and gravel and the deposition of fine particles downstream with rain, or the long-term erosion of rock and gravel in the river bed by water erosion. The product of this process is essentially clay, so the river silt is It has extremely high utilization value in the preparation of new building materials. The characteristics of clay minerals themselves also make their raw materials have a large plasticity index and good cohesion, which are suitable for industrial granulation into balls. At present, a large number of related researches mainly focus on the use of river silt to prepare new wall sintered bricks, or to replace shale to prepare sintered aggregates, etc. These methods can solve the problem of silt utilization to a certain extent, but their energy consumption is too high, exhaust gas Problems such as serious emissions and pollution limit the promotion and application of products.
发明内容SUMMARY OF THE INVENTION
本发明的目的是提供一种河道淤泥人造集料及其制备方法。The purpose of this invention is to provide a kind of artificial aggregate of river silt and preparation method thereof.
一种河道淤泥人造集料及其制备方法,首先将原料钙硅比控制在0.18~0.32;其次所用河道淤泥经初步压滤脱水至含水率为40±2%,成型过程无需额外加水,具体配比按人造集料质量百分比计,水泥:河道淤泥:石英尾矿:粉煤灰=10~15:55~70:9~25:6~10,其中,碳酸钠按人造集料质量1.0~3.0%以外加方式掺入,包含以下六个步骤:An artificial aggregate of river silt and a preparation method thereof, firstly, the calcium-silicon ratio of the raw material is controlled to be 0.18-0.32; secondly, the used river silt is dehydrated to a moisture content of 40±2% through preliminary pressure filtration, and no additional water is required in the molding process. According to the mass percentage of artificial aggregate, cement: river silt: quartz tailings: fly ash = 10-15: 55-70: 9-25: 6-10, of which, sodium carbonate is 1.0-3.0% by mass of artificial aggregate Incorporation in an additive manner involves the following six steps:
第一步:first step:
按配合比将干燥的石英尾矿、粉煤灰和外掺剂碳酸钠混合后置于球磨机中研磨,细度达到300目筛余小于15%,由此得到河道淤泥的干性激发剂;The dry quartz tailings, fly ash and admixture sodium carbonate are mixed according to the mixing ratio and then ground in a ball mill, and the fineness reaches 300 mesh and the sieve residue is less than 15%, thereby obtaining a dry activator for river silt;
第二步:Step 2:
将水泥、河道淤泥(压滤脱水后)和干性激发剂三种主要原料混合后置入专门搅拌粘性物料的槽式混合机中,充分搅拌10~15min,该过程无需额外加水,混合物料将逐渐进入可塑状态;Mix the three main raw materials, cement, river sludge (after dehydration by pressure filtration) and dry activator, and put them into a trough mixer specially designed for stirring viscous materials, and stir them thoroughly for 10-15 minutes. This process does not require additional water, and the mixture will be gradually enter a plastic state;
第三步:third step:
将搅拌完成的可塑物料倒入旋转挤压造粒机中,物料从直径10cm的漏板模具中缓慢挤出,经由外部旋转叶片打断后,获得5-10mm长的圆柱段体并落入位于下游持续旋转的盘式成球机中;Pour the stirred plastic material into the rotary extrusion granulator, the material is slowly extruded from the bushing die with a diameter of 10cm, and after being interrupted by the external rotating blade, a 5-10mm long cylindrical section is obtained and falls into the In a disc balling machine that continuously rotates downstream;
第四步:the fourth step:
将磨细钢渣粉与第三步旋转造粒机挤出的圆柱段体共同加入旋转的盘式成球机中,该过程需适当调控钢渣的添加量,磨细钢渣粉的掺加量依圆柱段体滚动出水量而定,具体范围控制在相对人造集料质量的6%~10%,持续加入钢渣粉直至集料的壳层完全成型,并继续滚动至转变为规则的圆球形,接着滚动5~10min,待到集料表面光滑且无粘连,料球粒径为5~15mm 时完成造粒过程;The ground steel slag powder and the cylindrical segment extruded from the rotary granulator in the third step are added to the rotating disc balling machine. In this process, the amount of steel slag added needs to be properly adjusted. The specific range is controlled at 6% to 10% of the mass of the artificial aggregate, and the steel slag powder is continuously added until the shell layer of the aggregate is completely formed, and the rolling is continued until it turns into a regular spherical shape, and then rolling 5-10min, when the aggregate surface is smooth and no adhesion, and the particle size of the pellets is 5-15mm, the granulation process is completed;
第五步:the fifth step:
将上述包壳后的淤泥集料放置阴凉处自然养护;The sludge aggregate after the above-mentioned cladding is placed in a cool place for natural conservation;
第六步:Step 6:
将自然养护后的物料置于蒸压釜中,在温度180~200℃、饱和蒸汽压1.0~1.5MPa的条件下连续水热合成反应8~10h,使之内部钙硅铝水四元体系反应生成高温水化相托贝莫来石(TOB) 以及水石榴石,即可得到所述人造集料。The material after natural curing is placed in an autoclave, and the continuous hydrothermal synthesis reaction is carried out under the conditions of temperature 180-200 ° C and saturated steam pressure 1.0-1.5 MPa, so that the internal calcium-silicon-aluminum water quaternary system is reacted. The artificial aggregate can be obtained by generating high temperature hydration phase tobermorite (TOB) and water garnet.
较佳的,第三步中,挤出圆柱段体的跌落高度不得高于1m,可由斜长型料槽连接至旋转的盘式成球机中。Preferably, in the third step, the drop height of the extruded cylindrical segment body should not be higher than 1m, which can be connected to the rotating disc-type ball-forming machine by an obliquely long trough.
较佳的,第五步中,将包壳后的物料放置阴凉处自然养护24h。Preferably, in the fifth step, the shelled material is placed in a cool place for natural curing for 24 hours.
较佳的,粉煤灰为国家一级粉煤灰;石英尾矿为石英砂磁选工艺产生的粒径小于0.125mm 的尾砂;水泥为普通硅酸盐水泥,标号PⅡ52.5;磨细钢渣粉为磨细转炉钢渣粉末,细度要求为300目,筛余小于15%。Preferably, the fly ash is national first-class fly ash; the quartz tailings are tailings with a particle size smaller than 0.125mm produced by the magnetic separation process of quartz sand; The steel slag powder is a finely ground converter steel slag powder, the fineness is required to be 300 mesh, and the sieve residue is less than 15%.
与现有技术相比,本发明具有以下优点:Compared with the prior art, the present invention has the following advantages:
(1)河道淤泥中除方石英外还含有斜绿泥石、白云母、伊利石等大量其他矿物。这些矿物都属于典型的粘土质矿物,具有粘土独特的表面吸附性与吸水膨胀性,其塑性指数超过12,具有十分良好的成球可塑性,本发明提出的人造集料制备工艺可工业化程度高;(2)本发明所述淤泥人造集料其形状为规则球型,球度较高,粒径集中分布在10~15mm之间。相比于形状不规则的建筑用碎石,球形的集料可以有效改善混凝土受压时的应力集中问题。该集料在混凝土中受力处于各项均匀状态,极限载荷大大提高,而碎石则容易在尖角棱边处形成应力集从而受到多向剪切力,混凝土强度表现反而下降;(3)本发明所述淤泥人造集料所用原料均为工业固废或者尾矿,其获取成本较为低廉,同时也为解决固废堆积的问题开辟了崭新思路;(4)本发明所述淤泥人造集料采用槽式混合机塑性捏合、挤出造粒、钢渣粉吸水造壳,形成核壳结构,其表层的结构修饰具有两大优点。一是改善了单个集料的受力结构,将点应力均匀分散为面应力有效防止集料受力劈裂问题,从而提高了集料本身筒压强度,二是提供一个活性表面,混凝土基体与集料之间产生牢固的界面结合力,从而消除了混凝土的界面薄弱区;(5)本发明所述淤泥人造集料在粘土质材料的合成体系中,摒弃了传统的烧结工艺,采用了蒸压合成工艺,并成功制备出了符合国家轻集料规范的人造淤泥集料。该工艺的改进使得本发明生产能耗极大降低,在理论能量转换率下,合成相同质量的人造集料,蒸压工艺相比烧结工艺可减少能耗80%,符合国家节能减排,绿色可持续的长久发展战略;(6)本发明所述淤泥人造集料性能十分优异。其表观密度低于1900kg/m3,堆积密度低于1000kg/m3,筒压强度均在16~22MPa之间。2h吸水率5~10%,冻融循环质量损失均小于5%,坚固性测试结果参照GB14685-2011《建设用卵石、碎石》评定为国家I类标准。(7)本发明所述淤泥人造集料具有优异的热工性能,在相同配合比下普通碎石混凝土导热系数为1.71W/(m·K),而淤泥集料等体积替换碎石后混凝土导热系数仅为0.85W/(m·K),相比之下保温性能可提升50%。(1) In addition to cristobalite, the river silt also contains a large number of other minerals such as plagiochlorite, muscovite, and illite. These minerals are all typical clay minerals, have the unique surface adsorption and water swellability of clay, their plasticity index exceeds 12, and have very good ball-forming plasticity, and the artificial aggregate preparation process proposed by the present invention has a high degree of industrialization; (2) The silt artificial aggregate of the present invention has a regular spherical shape, high sphericity, and a concentrated distribution of particle diameters between 10 and 15 mm. Compared with irregularly shaped crushed stones, spherical aggregates can effectively improve the stress concentration of concrete under compression. The aggregate is in a uniform state of stress in the concrete, and the ultimate load is greatly improved, while the crushed stone is easy to form a stress concentration at the sharp corner edge and is subjected to multi-directional shear force, and the strength of the concrete decreases instead; (3) The raw materials used in the silt artificial aggregates of the present invention are industrial solid waste or tailings, and the acquisition cost is relatively low, and at the same time, a new idea is opened for solving the problem of solid waste accumulation; (4) The silt artificial aggregates of the present invention are The core-shell structure is formed by plastic kneading, extrusion granulation and steel slag powder water absorption to form a core-shell structure. The structural modification of the surface layer has two major advantages. One is to improve the stress structure of a single aggregate, and the point stress is evenly dispersed into surface stress to effectively prevent the problem of aggregate splitting under force, thereby improving the cylinder compressive strength of the aggregate itself. The second is to provide an active surface. A firm interface bonding force is generated between the aggregates, thereby eliminating the weak interface area of the concrete; (5) In the synthesis system of the clay material, the silt artificial aggregate of the present invention abandons the traditional sintering process and adopts the steaming process. Press synthesis process, and successfully prepared man-made silt aggregates that meet the national light aggregate specifications. The improvement of the process greatly reduces the production energy consumption of the present invention. Under the theoretical energy conversion rate, artificial aggregates of the same quality can be synthesized. Compared with the sintering process, the autoclaving process can reduce the energy consumption by 80%, which is in line with national energy conservation and emission reduction, and is green Sustainable long-term development strategy; (6) The performance of the silt artificial aggregate of the present invention is very excellent. The apparent density is lower than 1900kg/m 3 , the bulk density is lower than 1000kg/m 3 , and the cylinder compressive strength is between 16-22MPa. The 2h water absorption rate is 5-10%, and the mass loss of the freeze-thaw cycle is less than 5%. The firmness test results are rated as the national class I standard according to GB14685-2011 "Pebbles and Crushed Stones for Construction". (7) The silt artificial aggregate of the present invention has excellent thermal performance, and the thermal conductivity of ordinary crushed stone concrete is 1.71W/(m·K) under the same mixing ratio, and the concrete after the crushed stone is replaced by the same volume of silt aggregate The thermal conductivity is only 0.85W/(m·K), and the thermal insulation performance can be improved by 50%.
附图说明Description of drawings
图1为为河道淤泥的XRD分析图谱。Fig. 1 is the XRD analysis pattern of the river silt.
图2为托贝莫来石(TOB)结构示意图。Figure 2 is a schematic diagram of the structure of tobermullite (TOB).
图3为托贝莫来石(TOB)晶体形貌SEM。Figure 3 is a SEM of the tobermullite (TOB) crystal morphology.
图4为水石榴石晶体形貌SEM。Figure 4 is a SEM of the crystal morphology of water garnet.
图5为本发明所述河道淤泥人造集料制备流程图。Fig. 5 is a flow chart of the preparation of the artificial aggregate of river silt according to the present invention.
具体实施方式Detailed ways
为了更了解本发明的技术内容,特列举具体实施例并配合附图说明如下。In order to better understand the technical content of the present invention, specific embodiments are given and described below in conjunction with the accompanying drawings.
在本发明中参照附图来描述本发明的各方面,附图中示出了本发明的实施例。本发明的实施例不必定意在包括本发明的所有方面。应当理解,上面介绍的多种构思和实施例,以及下面更加详细地描述的那些构思和实施方式可以以很多方式中任意一种来实施,这是因为本发明所公开的构思和实施例并不限于任何实施方式。另外,本发明公开的一些方面可以单独使用,或者与本发明公开的其他方面的任何适当组合来使用。Aspects of the invention are described herein with reference to the accompanying drawings, in which embodiments of the invention are shown. Embodiments of the invention are not necessarily intended to include all aspects of the invention. It should be understood that the various concepts and embodiments described above, as well as those described in greater detail below, can be implemented in any of a number of ways, as the concepts and embodiments disclosed herein do not limited to any implementation. Additionally, some aspects of the present disclosure may be used alone or in any suitable combination with other aspects of the present disclosure.
本发明的人造集料具备以下特点:一是成分梯度上包含内核-壳层两个部分,内核成分组成按质量比计算分别为水泥10%~15%,河道淤泥55%~70%,石英尾矿9%~25%,粉煤灰 6%~10%,外掺激发剂碳酸钠1%~3%,壳层成分为磨细钢渣粉;二是石英尾矿、粉煤灰和外掺剂按配比直接混合后球磨制备成干性激发剂,保证了激发活性;三是采用了可高度自动化的挤压成球法,成球效率高、成本低;四是采用免烧结的水热合成工艺养护人造集料,相比于传统粘土烧结集料该生产方式可节能80%。The artificial aggregate of the present invention has the following characteristics: firstly, the composition gradient contains two parts: the inner core and the shell layer, and the composition of the inner core is 10% to 15% of cement, 55% to 70% of river silt, and quartz tail. 9% to 25% of ore, 6% to 10% of fly ash, 1% to 3% of sodium carbonate as an external activator, and the shell composition is ground steel slag powder; the second is quartz tailings, fly ash and external admixtures The dry activator is prepared by ball milling after direct mixing according to the proportion, which ensures the activation activity; the third is the use of a highly automated extrusion method, which has high efficiency and low cost; the fourth is the use of a sinter-free hydrothermal synthesis process Compared with the traditional clay sintered aggregate, this production method can save energy by 80%.
本发明原理与设计构思是:The principle and design concept of the present invention are:
(1)长三角地区处于长江流域的中下游地区,长江支流众多地形复杂,且长期以来大量岩石风化随雨水流入河道,外加农业生产习惯的改变,河道淤泥更容易在该地区产生淤积。本发明以水热合成工艺开发利用含粘土矿物的原料,目的在于降低能耗并回收固废。(1) The Yangtze River Delta region is located in the middle and lower reaches of the Yangtze River Basin. There are many tributaries of the Yangtze River with complex topography, and for a long time, a large amount of rock weathering has flowed into the river channel with rainwater. In addition, changes in agricultural production habits make it easier for river silt to accumulate in this area. The present invention develops and utilizes raw materials containing clay minerals by a hydrothermal synthesis process, and aims to reduce energy consumption and recover solid waste.
(2)多体系水热合成反应(2) Multi-system hydrothermal synthesis reaction
河道淤泥的EDS结果表明,主要元素为SiO2,相对质量占比超过50%,其余Al2O3、Fe2O3、 MgO三种元素的占比总和达到30%。结合XRD结果可知,其内部存在方石英、斜绿泥石、伊利石、白云母等多种物相,其中斜绿泥石、伊利石、白云母属于粘土矿物,实验结果表明粘土矿物参与了最终的水热合成反应,该水化体系为钙硅铝氧四元反应体系。反应的主要水化产物为结晶良好的托贝莫来石(TOB)和水石榴石。其中TOB主要由CSH(B)过渡生成,TOB 是结晶态良好的CSH(B),具有层链状结构(图2),强度较高,SEM通常呈纤维状或者针片状(见图3)。而水化石榴石主要以河道淤泥中的白云母和斜绿泥石作为铝源合成。水石榴石在SEM中呈八面体颗粒(见图4),同样具有较高强度,少量存在时可以提升人造集料强度。The EDS results of the river silt show that the main element is SiO 2 , which accounts for more than 50% of the relative mass, and the total proportion of the remaining three elements, Al 2 O 3 , Fe 2 O 3 and MgO, reaches 30%. Combined with the XRD results, it can be seen that there are various phases such as cristobalite, clinochlorite, illite, and muscovite, among which clinochlorite, illite, and muscovite belong to clay minerals. The experimental results show that clay minerals are involved in the final phase. The hydrothermal synthesis reaction of the hydration system is a calcium-silicon-aluminum-oxygen quaternary reaction system. The main hydration products of the reaction are well-crystallized tobermorite (TOB) and water garnet. Among them, TOB is mainly generated by transition of CSH (B), TOB is CSH (B) with good crystalline state, with layered chain structure (Fig. 2), high strength, SEM is usually fibrous or needle-like (see Fig. 3) . The hydrated garnet is mainly synthesized from muscovite and clinochlorite in river silt as aluminum sources. Water garnet is octahedral particles in SEM (see Figure 4), and also has high strength, and the presence of a small amount can improve the strength of artificial aggregates.
(3)本发明制备所述淤泥集料,将石英尾矿、粉煤灰和外掺剂进行混合球磨处理制备成干性激发剂,可以提高混合均匀性。粘土本身颗粒细小,但由于具有表面负电性而容易发生与其他颗粒的团聚,因而不易分散。该工艺可以起到调控粘度,控制成球效率的关键作用。(3) The sludge aggregate is prepared by the present invention, and the quartz tailings, fly ash and external admixture are mixed and ball-milled to prepare a dry activator, which can improve the mixing uniformity. Clay itself has fine particles, but because of its negative surface charge, it is easy to agglomerate with other particles, so it is not easy to disperse. This process can play a key role in regulating viscosity and controlling the efficiency of ball formation.
(4)本发明所述淤泥人造集料具有核壳结构,包壳成分为磨细钢渣粉,包壳灰质量占人造集料质量的6~10%。包壳过程可修饰集料表层结构,使其表面粗糙,形成活性界面,使得混凝土内部形成骨料-基体活性界面,有效防止混凝土受压时裂纹在界面处失稳扩散。(4) The silt artificial aggregate of the present invention has a core-shell structure, the cladding component is ground steel slag powder, and the mass of the cladding ash accounts for 6-10% of the mass of the artificial aggregate. The cladding process can modify the surface structure of the aggregate, make the surface rough, and form an active interface, so that an active interface between the aggregate and the matrix is formed inside the concrete, which effectively prevents the cracks from spreading at the interface when the concrete is compressed.
(5)本发明所述淤泥人造集料,采用挤出成型法制备淤泥集料,充分利用了河道淤泥粘塑性高的特点。采用该方法制备人造集料可极大的提高制备效率与成型均匀性,可工业化程度极高。(5) The silt artificial aggregate of the present invention adopts the extrusion molding method to prepare the silt aggregate, which makes full use of the characteristics of high viscoplasticity of river silt. Using this method to prepare artificial aggregate can greatly improve the preparation efficiency and molding uniformity, and the degree of industrialization is extremely high.
本发明以河道淤泥作为原材料,开展淤泥人造集料制备,对淤泥的主要矿物相进行测试, XRD衍射图谱表明(见图1),主要物相为方石英以及白云母,伊利石,斜绿泥石等粘土类非金属矿物。The present invention uses river silt as a raw material, carries out the preparation of silt artificial aggregates, tests the main mineral phases of the silt, and the XRD diffraction pattern shows (see Fig. 1) that the main phases are cristobalite and muscovite, illite, and oblique green mud. Clay non-metallic minerals such as stone.
下面结合图5阐述本发明的制备过程。使用原材料化学成分见表1。The preparation process of the present invention will be described below with reference to FIG. 5 . The chemical composition of the raw materials used is shown in Table 1.
表1河道淤泥、石英尾矿和粉煤灰的主要化学成分(wt.%)Table 1 Main chemical components of river silt, quartz tailings and fly ash (wt.%)
实施例1:Example 1:
一种本发明所述淤泥人造集料,具体质量配比为:水泥:河道淤泥:石英尾矿:粉煤灰= 15:70:9:6;碳酸钠掺量3.0wt%(钙硅比0.23),其具体制备过程包含以下步骤:A silt artificial aggregate of the present invention, the specific mass ratio is: cement: river silt: quartz tailings: fly ash = 15:70:9:6; sodium carbonate dosage 3.0wt% (calcium-silicon ratio 0.23 ), and its specific preparation process comprises the following steps:
第一步:first step:
按配合将干燥的石英尾矿90kg、粉煤灰60kg和碳酸钠30kg混合后置于球磨机中研磨,原料细度300目筛余小于15%,由此得到河道淤泥的干性激发剂;90kg of dry quartz tailings, 60kg of fly ash and 30kg of sodium carbonate are mixed according to the coordination and then placed in a ball mill for grinding, and the sieve residue of the 300-mesh raw material is less than 15%, thereby obtaining a dry activator for river silt;
第二步:Step 2:
称取水泥150kg、河道淤泥(压滤脱水后)700kg和干性激发剂150kg混合后置入专门搅拌粘性物料的槽式混合机中,充分搅拌10min,该过程无需额外加水,混合物料将逐渐进入可塑状态;Weigh 150kg of cement, 700kg of river silt (after dehydration by filter press), and 150kg of dry activator, and put them into a tank mixer specially designed for stirring viscous materials, and stir them fully for 10 minutes. No additional water is needed in this process, and the mixture will gradually enter plastic state;
第三步:third step:
将搅拌完成的可塑物料倒入旋转挤压造粒机中,物料从直径10cm的漏板模具中缓慢挤出,经由外部旋转叶片打断后,获得5~10mm长的圆柱段体并落入位于下游持续旋转的盘式成球机中;Pour the stirred plastic material into the rotary extrusion granulator, the material is slowly extruded from the bushing die with a diameter of 10cm, and after being interrupted by the external rotating blade, a cylindrical section with a length of 5-10mm is obtained and falls into the In a disc balling machine that continuously rotates downstream;
第四步:the fourth step:
将60kg磨细钢渣粉与第三步旋转造粒机挤出的圆柱段共同加入旋转的盘式成球机中,持续加入钢渣粉直至集料的壳层完全成型,并继续滚动至转变为规则的圆球形,接着滚动 10min,待到集料表面光滑且无粘连时完成造粒过程,料球粒径为5~15mm;Add 60kg of ground steel slag powder together with the cylindrical section extruded from the third-step rotary granulator into the rotating disc balling machine, continue to add steel slag powder until the shell layer of the aggregate is completely formed, and continue to roll until it becomes regular After rolling for 10 minutes, the granulation process is completed when the surface of the aggregate is smooth and there is no adhesion, and the particle size of the pellet is 5-15mm;
第五步:the fifth step:
将上述包壳后的淤泥集料放置阴凉处自然养护;The sludge aggregate after the above-mentioned cladding is placed in a cool place for natural conservation;
第六步:Step 6:
将自然养护后的物料置于蒸压釜中,在温度180℃、饱和蒸汽压1.0MPa的条件下连续水热合成反应10h,使之内部钙硅铝水四元体系反应生成高温水化相托贝莫来石(TOB)以及水石榴石,即可得到所述人造集料。The material after natural curing was placed in an autoclave, and the continuous hydrothermal synthesis reaction was carried out for 10 hours under the conditions of a temperature of 180 ° C and a saturated vapor pressure of 1.0 MPa, so that the internal calcium-silicon-aluminum water quaternary system was reacted to generate a high-temperature hydration phase. Bermulite (TOB) and water garnet can obtain the artificial aggregate.
采用本实施例制备的人造集料2h吸水率为9.1%,表观密度为1.79g/cm3;筒压强度达到 18.8MPa,软化系数0.87;冻融循环质量损失仅为0.4%,达到国家建筑用集料抗冻性标准;坚固性测试质量损失-1.3%,达到国家建筑用集料坚固性I类标准。The artificial aggregate prepared by this example has a 2h water absorption rate of 9.1%, an apparent density of 1.79g/cm 3 , a cylinder compressive strength of 18.8MPa, a softening coefficient of 0.87, and a freeze-thaw cycle mass loss of only 0.4%, reaching the national construction level The frost resistance standard of the aggregate; the mass loss of the solidity test is -1.3%, reaching the national class I standard of the solidity of the aggregate for construction.
实施例2:Example 2:
一种本发明所述淤泥人造集料,具体质量配比为:水泥:河道淤泥:石英尾矿:粉煤灰= 10:55:25:10;碳酸钠掺量1.0wt%(钙硅比0.25)其具体制备过程包含以下步骤:A silt artificial aggregate of the present invention, the specific mass ratio is: cement: river silt: quartz tailings: fly ash = 10:55:25:10; sodium carbonate dosage 1.0wt% (calcium-silicon ratio 0.25 ) its specific preparation process comprises the following steps:
第一步:first step:
按配合将干燥的石英尾矿250kg、粉煤灰100kg和碳酸钠10kg混合后置于球磨机中研磨,原料细度300目筛余小于15%,由此得到河道淤泥的干性激发剂;Mix 250kg of dry quartz tailings, 100kg of fly ash and 10kg of sodium carbonate according to the coordination and then place them in a ball mill for grinding, and the fineness of the raw materials is less than 15% of 300 mesh sieves, thereby obtaining a dry activator for river silt;
第二步:Step 2:
称取水泥100kg、河道淤泥(压滤脱水后)550kg和干性激发剂350kg混合后置入专门搅拌粘性物料的槽式混合机中,充分搅拌15min,该过程无需额外加水,混合物料将逐渐进入可塑状态;Weigh 100kg of cement, 550kg of river silt (after dehydration by filter press), and 350kg of dry activator, and put them into a trough mixer specially designed for stirring viscous materials, and stir them fully for 15 minutes. No additional water is required in this process, and the mixture will gradually enter plastic state;
第三步:third step:
将搅拌完成的可塑物料倒入旋转挤压造粒机中,物料从直径10cm的漏板模具中缓慢挤出,经由外部旋转叶片打断后,获得5~10mm长的圆柱段体并落入位于下游持续旋转的盘式成球机中;Pour the stirred plastic material into the rotary extrusion granulator, the material is slowly extruded from the bushing die with a diameter of 10cm, and after being interrupted by the external rotating blade, a cylindrical section with a length of 5-10mm is obtained and falls into the In a disc balling machine that continuously rotates downstream;
第四步:the fourth step:
将100kg磨细钢渣粉与第三步旋转造粒机挤出的圆柱段共同加入旋转的盘式成球机中,持续加入钢渣粉直至集料的壳层完全成型,并继续滚动至转变为规则的圆球形,接着滚动 5min,待到集料表面光滑且无粘连时完成造粒过程,料球粒径为5~15mm;Add 100kg of ground steel slag powder and the cylindrical section extruded from the third-step rotary granulator into the rotating disc balling machine, continue to add steel slag powder until the shell of the aggregate is completely formed, and continue to roll until it turns into a regular Then roll for 5 minutes, and complete the granulation process when the surface of the aggregate is smooth and without adhesion, and the particle size of the pellet is 5-15mm;
第五步:the fifth step:
将上述包壳后的淤泥集料放置阴凉处自然养护;The sludge aggregate after the above-mentioned cladding is placed in a cool place for natural conservation;
第六步:Step 6:
将自然养护后的物料置于蒸压釜中,在温度200℃、饱和蒸汽压1.5MPa的条件下连续水热合成反应10h,使之内部钙硅铝水四元体系反应生成高温水化相托贝莫来石(TOB)以及水石榴石,即可得到所述人造集料。The material after natural curing was placed in an autoclave, and the continuous hydrothermal synthesis reaction was carried out for 10 hours under the conditions of temperature of 200 ° C and saturated vapor pressure of 1.5 MPa, so that the internal calcium-silicon-aluminum water quaternary system was reacted to form a high-temperature hydration phase. Bermulite (TOB) and water garnet can obtain the artificial aggregate.
采用本实施例制备的人造集料2h吸水率为8.9%,表观密度为1.85g/cm3;筒压强度达到 18.5MPa,软化系数0.91;冻融循环质量损失仅为1.28%,达到国家建筑用集料抗冻性标准;坚固性测试质量损失-4.9%,达到国家建筑用集料坚固性I类标准。The artificial aggregate prepared by this example has a 2h water absorption rate of 8.9%, an apparent density of 1.85g/cm 3 , a cylinder compressive strength of 18.5MPa, a softening coefficient of 0.91, and a freeze-thaw cycle mass loss of only 1.28%, reaching the national construction level. The frost resistance standard of the aggregate; the mass loss of the solidity test is -4.9%, which reaches the national class I standard of the solidity of the aggregate for construction.
实施例3:Example 3:
一种本发明所述淤泥人造集料,具体质量配比为:水泥:河道淤泥:石英尾矿:粉煤灰= 12:63:17:8,碳酸钠掺量2.0%(钙硅比0.27),其具体制备过程包含以下步骤:A silt artificial aggregate of the present invention, the specific mass ratio is: cement: river silt: quartz tailings: fly ash = 12:63:17:8, sodium carbonate dosage 2.0% (calcium-silicon ratio 0.27) , and its specific preparation process includes the following steps:
第一步:first step:
按配合将干燥的石英尾矿170kg、粉煤灰80kg和碳酸钠20kg混合后置于球磨机中研磨,原料细度300目筛余小于15%,由此得到河道淤泥的干性激发剂;Mix 170kg of dry quartz tailings, 80kg of fly ash and 20kg of sodium carbonate according to the coordination and then place them in a ball mill to grind, and the sieve residue of the raw material fineness of 300 meshes is less than 15%, thereby obtaining a dry activator for river silt;
第二步:Step 2:
称取水泥120kg、河道淤泥(压滤脱水后)630kg和干性激发剂250kg混合后置入专门搅拌粘性物料的槽式混合机中,充分搅拌12min,该过程无需额外加水,混合物料将逐渐进入可塑状态;Weigh 120kg of cement, 630kg of river silt (after filter press dehydration), and 250kg of dry activator, put them into a tank mixer specially designed for stirring viscous materials, and stir them thoroughly for 12 minutes. This process does not require additional water, and the mixture will gradually enter plastic state;
第三步:third step:
将搅拌完成的可塑物料倒入旋转挤压造粒机中,物料从直径10cm的漏板模具中缓慢挤出,经由外部旋转叶片打断后,获得5~10mm长的圆柱段体并落入位于下游持续旋转的盘式成球机中;Pour the stirred plastic material into the rotary extrusion granulator, the material is slowly extruded from the bushing die with a diameter of 10cm, and after being interrupted by the external rotating blade, a cylindrical section with a length of 5-10mm is obtained and falls into the In a disc balling machine that continuously rotates downstream;
第四步:the fourth step:
将80kg磨细钢渣粉与第三步旋转造粒机挤出的圆柱段共同加入旋转的盘式成球机中,持续加入钢渣粉直至集料的壳层完全成型,并继续滚动至转变为规则的圆球形,接着滚动8 min,待到集料表面光滑且无粘连时完成造粒过程,料球粒径为5~15mm;Add 80kg of ground steel slag powder together with the cylindrical section extruded from the third-step rotary granulator into the rotating disc balling machine, continue to add steel slag powder until the shell layer of the aggregate is completely formed, and continue to roll until it becomes regular After rolling for 8 minutes, the granulation process is completed when the surface of the aggregate is smooth and there is no adhesion, and the particle size of the pellet is 5-15mm;
第五步:the fifth step:
将上述包壳后的淤泥集料放置阴凉处自然养护;The sludge aggregate after the above-mentioned cladding is placed in a cool place for natural conservation;
第六步:Step 6:
将自然养护后的物料置于蒸压釜中,在温度180℃、饱和蒸汽压1.0MPa的条件下连续水热合成反应10h,使之内部钙硅铝水四元体系反应生成高温水化相托贝莫来石(TOB)以及水石榴石,即可得到所述人造集料。The material after natural curing was placed in an autoclave, and the continuous hydrothermal synthesis reaction was carried out for 10 hours under the conditions of a temperature of 180 ° C and a saturated vapor pressure of 1.0 MPa, so that the internal calcium-silicon-aluminum water quaternary system was reacted to generate a high-temperature hydration phase. Bermulite (TOB) and water garnet can obtain the artificial aggregate.
采用本实施例制备的人造集料2h吸水率为9.9%,表观密度为1.86g/cm3;筒压强度达到21.9MPa,软化系数0.95;冻融循环质量损失仅为0.4%,达到国家建筑用集料抗冻性标准;坚固性测试质量损失-1.3%,达到国家建筑用集料坚固性I类标准。The artificial aggregate prepared by this example has a 2h water absorption rate of 9.9%, an apparent density of 1.86g/cm3, a cylinder compressive strength of 21.9MPa, a softening coefficient of 0.95, and a freeze-thaw cycle mass loss of only 0.4%, which is suitable for national construction. Aggregate frost resistance standard; solidity test mass loss -1.3%, reaching the national construction aggregate solidity class I standard.
对比例4:Comparative Example 4:
本对比例在本发明提出的合理配和比外选取方案制备人造集料,与实施例1~3形成鲜明对比。具体质量配比为:水泥:河道淤泥:石英尾矿:粉煤灰=14:80:3:3,碳酸钠掺量3.5%,具体制备过程与实施例1~3相同。In this comparative example, artificial aggregates are prepared by selecting a scheme other than the reasonable ratio and ratio proposed by the present invention, which is in sharp contrast with Examples 1-3. The specific mass ratio is: cement: river silt: quartz tailings: fly ash = 14:80:3:3, sodium carbonate dosage is 3.5%, and the specific preparation process is the same as in Examples 1-3.
采用本对比例制备的人造集料2h吸水率为12.9%,表观密度为1.81g/cm3;筒压强度仅为14.5MPa,软化系数仅为0.75,低于0.8的合格标准;冻融循环和坚固性测试均不达标;集料蒸压易开裂,上述性能均不符合生产制备要求。The artificial aggregate prepared by this comparative example has a 2-h water absorption rate of 12.9% and an apparent density of 1.81g/cm 3 ; the cylinder compressive strength is only 14.5MPa, and the softening coefficient is only 0.75, which is lower than the qualified standard of 0.8; the freeze-thaw cycle and the firmness test are not up to standard; the aggregate is prone to cracking under autoclave, and the above properties do not meet the production and preparation requirements.
实施例5:Example 5:
利用实施例1中的人造淤泥集料试配混凝土,配合比设计综合参考《轻骨料混凝土技术规程》JGJ 51-2002和《普通混凝土配合比设计规程》JGJ 55-2011,将其作为骨料制备混凝土试块,同时以碎石等体积取代所述淤泥集料,相同配合比下进行各项性能对比。实验配合比如下表所示:The artificial silt aggregate in Example 1 is used to prepare concrete, and the mix ratio design comprehensively refers to "Technical Specification for Lightweight Aggregate Concrete" JGJ 51-2002 and "Ordinary Concrete Mix Ratio Design Specification" JGJ 55-2011, which is used as aggregate A concrete test block was prepared, and at the same time, the sludge aggregate was replaced with an equal volume of crushed stone, and various properties were compared under the same mixing ratio. The experimental coordination ratio is shown in the following table:
表2人造集料-碎石混凝土对比实验设计配合比Table 2 Design mix ratio of artificial aggregate-gravel concrete comparative experiment
表3人造集料-碎石混凝土对比实验结果Table 3 Comparative experimental results of artificial aggregate-crushed stone concrete
此实施例中使用淤泥集料试配的轻集料混凝土的表观密度为2034.4kg/m3,仅相当于普通碎石混凝土表观密度的84.4%,减自重效果十分明显;淤泥集料混凝土28d抗压强度可达到69.8MPa,反而高于普通碎石混凝土,工程表现更佳;淤泥集料混凝土的导热系数仅为0.85 W/(m·K),相较于普通碎石混凝土,保温隔热性能提高50%。In this example, the apparent density of the light aggregate concrete prepared by using the silt aggregate is 2034.4kg/m 3 , which is only 84.4% of the apparent density of the ordinary gravel concrete, and the effect of reducing the self-weight is very obvious; the silt aggregate concrete The 28d compressive strength can reach 69.8MPa, which is higher than that of ordinary gravel concrete, and the engineering performance is better; the thermal conductivity of silt aggregate concrete is only 0.85 W/(m·K), compared with ordinary gravel concrete, thermal insulation Thermal performance increased by 50%.
本发明充分利用河道淤泥内含有的方石英、伊利石、白云母、斜绿泥石等物相,在成型工艺上采用搅拌成球法以及包壳修饰等技术改善成型均匀性;在养护工艺上通过钙硅铝水四元水化反应合成高温水化相托贝莫来石(TOB)(见图3)以及水石榴石(见图4)提高集料强度,最终制备出兼具强度,多孔特性和保温隔热特性的新型人造集料。本发明回收河道淤泥方案也同样适用于长江流域地区工程建设产生的盾构渣土、基坑渣土以及钻孔渣土等典型渣土类建筑垃圾。The invention makes full use of the phases of cristobalite, illite, muscovite, clinochlorite and the like contained in the river silt, and adopts technologies such as stirring into a ball method and cladding modification in the molding process to improve the uniformity of molding; The high-temperature hydration phase tobermullite (TOB) (see Figure 3) and water garnet (see Figure 4) were synthesized through the quaternary hydration reaction of calcium-silicon-alumina water to improve the strength of the aggregates, and finally a porous, porous material with both strength was prepared. New man-made aggregates with properties and thermal insulation properties. The scheme for recovering river silt in the present invention is also applicable to typical slag construction wastes such as shield slag, foundation pit slag and drilling slag produced by engineering construction in the Yangtze River Basin.
本发明利用脱水处理的河道淤泥制备人造集料,通过调整配合比,混合多种硅质材料,采用水热合成工艺,既提高了人造集料力学性能,又降低了生产能耗。因此,本发明技术的最大优势在于可以工业化集中处理河道淤泥,同时生产出具有高附加值的人造集料,产生双重经济效益。以本发明专利制备的人造集料可以完全适配LC60高标号轻集料混凝土,不仅抗压强度高,热工性能还十分良好,对于河道淤泥的资源化利用具有十分重要的意义。The method utilizes dewatered river silt to prepare artificial aggregates, adjusts the mixing ratio, mixes various siliceous materials, and adopts a hydrothermal synthesis process, which not only improves the mechanical properties of artificial aggregates, but also reduces production energy consumption. Therefore, the biggest advantage of the technology of the present invention is that it can industrially and intensively process the river silt, and at the same time, it can produce artificial aggregates with high added value, thereby generating double economic benefits. The artificial aggregate prepared with the patent of the present invention can be fully adapted to LC60 high-grade lightweight aggregate concrete, not only has high compressive strength, but also has very good thermal performance, which is of great significance for the resource utilization of river silt.
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