CN1034148A - Rubbish is transformed into a kind of method of grain shape material - Google Patents
Rubbish is transformed into a kind of method of grain shape material Download PDFInfo
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- CN1034148A CN1034148A CN88107505A CN88107505A CN1034148A CN 1034148 A CN1034148 A CN 1034148A CN 88107505 A CN88107505 A CN 88107505A CN 88107505 A CN88107505 A CN 88107505A CN 1034148 A CN1034148 A CN 1034148A
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B1/00—Dumping solid waste
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/30—Destroying solid waste or transforming solid waste into something useful or harmless involving mechanical treatment
- B09B3/32—Compressing or compacting
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/30—Destroying solid waste or transforming solid waste into something useful or harmless involving mechanical treatment
- B09B3/35—Shredding, crushing or cutting
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/70—Chemical treatment, e.g. pH adjustment or oxidation
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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
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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
- C04B18/04—Waste materials; Refuse
- C04B18/30—Mixed waste; Waste of undefined composition
- C04B18/305—Municipal waste
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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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- Processing Of Solid Wastes (AREA)
- Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
- Treatment Of Sludge (AREA)
- Glanulating (AREA)
Abstract
把垃圾转变为一种颗粒材料的方法,其特征在 于,由粉碎垃圾,实际上是去除了所有金属块的粉碎 垃圾与至少一种含游离态或化合态氧化钙的粉状矿 物质混合制备均匀混合物;将此混合物制成压缩体形 式;压缩体被加热、干燥、硬化;粉碎干燥硬化的压缩 体,制成由粒状颗粒和纤维混合物组成的分得很细的 材料;对此材料进行附聚处理制成颗粒形状。这种颗 粒可用于生产建筑材料。A method of converting waste into a granular material characterized by Yu, by shredding garbage, is actually shredding that removes all the metal pieces Garbage and at least one powdery ore containing free or combined calcium oxide To mix substances to prepare a homogeneous mixture; to form this mixture into a compressed form formula; the compressed body is heated, dried, and hardened; the crushed dry hardened compressed bodies, made of finely divided mixtures of granular particles and fibers Material; this material is agglomerated to produce granular shapes. this grain Granules can be used to produce building materials.
Description
本发明涉及把垃圾转变成一种颗粒形状材料的方法。更具体地讲,本方法能把垃圾,特别是生活垃圾转变成既防腐又不溶于水的坚硬颗粒,可用于诸如砖之类的建筑材料的生产或用作制备混凝土的一种集料。The present invention relates to a method of converting waste into a granular form material. More specifically, the method converts waste, especially domestic waste, into hard particles that are both corrosion-resistant and insoluble in water, which can be used in the production of building materials such as bricks or as an aggregate for the preparation of concrete.
众所周知,由于在清除数量不断增加的垃圾和废物的同时还必须防止污染和其他公害,此问题越来越难以解决。This problem is notoriously difficult to solve due to the need to prevent pollution and other nuisances while removing ever-increasing amounts of litter and waste.
为了提供一种可接受的解决这些问题的方法,有人提出,把事先粉碎的,已去除可能包含的金属的垃圾转变成一种可用作建筑材料的各种形式各种尺寸的固体。In order to provide an acceptable solution to these problems, it has been proposed to convert previously shredded waste from which any metals it may contain may be converted into a solid of various forms and sizes which may be used as a construction material.
例如,法国专利2098777号描述了可用作建筑材料或填充材料的硬质坚实块料的制备方法:将一种金属硅酸盐加到一堆未分类的粉碎的垃圾中,在压模中将这堆垃圾在高压下做压缩处理,制成块料形式,最后或者在室温下,或者在比如80-200℃温度下加热,将块料硬化。For example, French Patent No. 2098777 describes the preparation of hard solid blocks that can be used as building materials or filling materials: a metal silicate is added to a pile of unsorted comminuted waste, and the This pile of waste is compressed under high pressure into block form, and finally the block is hardened by heating either at room temperature or at a temperature of, say, 80-200°C.
法国专利申请2286116号介绍了一种从去除了金属成份、干燥粉碎的垃圾中制备园筒型集料的方法,以代替混凝土生产中的天然砾石。按照实施本方法的一个例子,垃圾粉碎粉同一种防腐烂保护剂如金属硅酸盐或糠醛,一种粘合剂如一种合成树脂,一种可溶性沥青或生石灰,矿石渣以及一种粘合剂硬化催化剂混合,制成稠糊状,经压模压成园筒形压缩体,最后这些压缩体在最高不超过200℃的温度下加热进行硬化。French Patent Application No. 2286116 describes a method for preparing cylindrical aggregates from demetallized, dry and comminuted waste to replace natural gravel in concrete production. According to an example of carrying out the method, the rubbish pulverized powder is combined with an anti-rot protection agent such as metal silicate or furfural, a binder such as a synthetic resin, a soluble bitumen or quicklime, ore slag and a binder The hardening catalyst is mixed to make a thick paste, which is pressed into a cylindrical compressed body by compression molding, and finally these compressed bodies are heated at a temperature not exceeding 200°C for hardening.
按照上述文献提到的现有技术的方法并不完全令人满意,主要是因为这些方法不能保证所得固体(有很好的机械性能)具有高的生物惰性和化学惰性,同时也不能保证在实用中在水中的溶解度为零,而在作为建筑材料的使用中很需要这些性能。The methods according to the prior art mentioned in the above-mentioned documents are not completely satisfactory, mainly because these methods cannot guarantee that the resulting solid (with good mechanical properties) has high biological and chemical inertness, and at the same time cannot guarantee The solubility in water is zero, and these properties are very much needed in the use as a building material.
本发明的目的是把大量的垃圾转变成既防腐,在实用中又不溶于水的硬质颗粒。所用垃圾未经分类,仅用已知方法将垃圾中可能含有的金属成分,特别是金属铁去除,然后粉碎。为了这一目的,按照本发明的方法具有权利要求1所陈述的特点。The purpose of the invention is to convert a large amount of rubbish into hard granules which are both anti-corrosion and practically insoluble in water. The garbage used is not sorted, and only the metal components that may be contained in the garbage, especially metallic iron, are removed by known methods and then pulverized. For this purpose, the method according to the invention has the features stated in claim 1 .
因此,按照本发明,这一方法基于以下几个过程,对压缩体(在压力下对主要是由粉碎垃圾和含氧化钙的矿物材料组成的均匀混合物进行制粒作用制得)进行热处理,对这些成分磨碎或粉碎制成由颗粒和纤维组成的细粉料,最后细粉料附聚成颗粒形式。Therefore, according to the invention, the method is based on the following processes, the thermal treatment of compacted bodies (produced by granulation under pressure of a homogeneous mixture mainly composed of comminuted waste and calcium oxide-containing mineral material), the These ingredients are ground or pulverized to form a fine powder consisting of particles and fibers, which is finally agglomerated into granular form.
人们惊奇地发现,这种操作过程的新组合方式能得到既具有高机械阻又具有高化学惰性和高生物惰性,同时在水中的溶解度几乎为零的颗粒,因此这些颗粒有可能用于许多各种有用的用途,特别是生产建筑材料,而不会产生任何污染和其他公害。It has been surprisingly found that this new combination of operations yields particles with high mechanical resistance, high chemical inertness, high biological inertness, and almost zero solubility in water, so that these particles have the potential to be used in many different applications. a useful use, especially for the production of construction materials, without any pollution and other nuisances.
含有自由态或化合态氧化钙的矿物质可以从比如生石灰,方解石,石灰岩和粘土质材料中选择。Minerals containing free or combined calcium oxide may be selected from materials such as quicklime, calcite, limestone and clay.
在粉碎垃圾和含氧化钙矿物质的混合物中,垃圾含量最好为90-95%(重量),矿物质含量为5-10%(重量)。In the mixture of pulverized waste and calcium oxide-containing minerals, the waste content is preferably 90-95% by weight and the mineral content is 5-10% by weight.
而且,粉碎的垃圾或磨碎的垃圾和含氧化钙矿物质的混合物可以与各种填料,特别是含自由态或化合态碳酸钙和碳酸镁矿物质,比如白云石,进行混合。Furthermore, comminuted refuse or a mixture of ground refuse and calcium oxide-containing minerals can be mixed with various fillers, especially minerals containing free or combined calcium and magnesium carbonates, such as dolomite.
实施本发明方法的不同操作,可以用任何合适的方法进行,特别是使用已知技术和普通设备处理垃圾。The various operations for carrying out the method of the invention may be carried out in any suitable way, in particular for waste disposal using known techniques and common equipment.
特殊地,为了得到实际上不含有金属成分的垃圾,可以使用收集箱中的垃圾或废物经通常的分类、过筛操作,以便从中分出可以回收和/或重复使用的物体,特别是大块金属。In particular, in order to obtain rubbish that is practically free of metal components, it is possible to use the usual sorting and sieving operations of rubbish or waste in collection bins, in order to separate objects that can be recycled and/or reused, especially large pieces Metal.
此后,为了使垃圾成为实际上不含有金属材料(特别是铁)的均匀粉状混合物,可以同时或分别地对垃圾进行粉碎和混合操作,可能时,与一个或多个旨在分离出金属块特别是含铁碎块的分类操作相结合。例如对已分类的垃圾进行初级粗粉碎,使碎块平均大小约50毫米,此粉碎操作是在为除去铁粒和其他铁磁性材料的磁性分类之前或之后进行。然后利用例如旋转锤、粉碎机或撕碎机进行第二次粉碎,以使垃圾变为最大直径小于20毫米的颗粒或纤维形式的微粒。Thereafter, the rubbish may be comminuted and mixed simultaneously or separately in order to obtain a homogeneous powdery mixture practically free of metallic materials (especially iron) and, where possible, with one or more In particular the sorting operation of ferrous fragments is combined. For example, the primary coarse crushing of sorted waste, so that the average size of the fragments is about 50 mm, is carried out before or after magnetic sorting to remove iron particles and other ferromagnetic materials. A second comminution is then carried out using, for example, rotary hammers, pulverizers or shredders to reduce the waste to fine particles in the form of granules or fibers with a maximum diameter of less than 20 mm.
大量粉碎垃圾和含氧化钙矿物质的混合操作也可以使用任何适当技术和设备,特别是使用配料器和可以连续或间歇运转的自动混合器。The mixing operation of the bulk crushed waste and calcium oxide-containing minerals may also use any suitable technique and equipment, in particular the use of batchers and automatic mixers which may operate continuously or intermittently.
由粉碎垃圾和含氧化钙矿物质的混合物制备压缩体,可以使用配有滚子和压模的旋转制粒装置(比如,生产颗粒状动物饲料的设备),在150-900巴的压力下制粒,制成例如长度为5-60毫米,直径为2-20毫米的园筒形压缩体。Compressed bodies prepared from a mixture of comminuted waste and calcium oxide-containing minerals, which can be produced at a pressure of 150-900 bar using a rotary granulation unit (e.g. for the production of pelleted animal feed) equipped with rollers and dies Granules, made into, for example, a cylindrical compressed body with a length of 5-60 mm and a diameter of 2-20 mm.
最好是将压缩体轴向通过具有水平旋转轴的管式旋转窑进行压缩体的热处理,所说的窑由热空气加热,其内部具有螺旋壁以保证压缩体的流通。特别地,可以使用有热空气流穿过的窑或炉,热空气流是用燃烧器加热至250-400℃温度范围的,其流动方向与压缩体的流动方向一致。The heat treatment of the compressed body is preferably carried out by passing the compressed body axially through a tubular rotary kiln with a horizontal axis of rotation, said kiln being heated by hot air and having spiral walls inside to ensure the circulation of the compressed body. In particular, it is possible to use a kiln or furnace through which a flow of hot air, heated with burners to a temperature in the range of 250-400° C., flows in the same direction as that of the compressed body.
这种处理的作用是将压缩体中水的含量降为例如5%(重量),并通过氧化钙转化为碳酸钙的碳化作用增大压缩体的硬度。经过干燥和硬化后,压缩体可以以任何适当的方法,特别地,使用可拆卸的带有筛网(使粉碎的材料通过)的锤式粉碎机进行粉碎。这样得到的是含有某一比例的纤维材料(由初始垃圾中的比如纺织品、塑料和纤维素材料得来)和某一比例的由粉碎矿物质(垃圾中的比如玻璃,石灰石等或有机物质)得到的粒状颗粒的细分材料。纤维材料的长度或是通过改变压缩体的粉碎或磨碎条件或是通过调整纤维长度的后续操作如筛选操作,进行调整,使大多数纤维长度在给定的范围内,最好是在0.1-30毫米之间。例如,在粉碎压缩体时,通过选择合适的磨碎机筛网的细度如1-4毫米,可以调整纤维的长度,综合地讲可以调整细分材料的尺寸。The effect of this treatment is to reduce the water content of the compact to eg 5% by weight and to increase the hardness of the compact by carbonization of the calcium oxide into calcium carbonate. After drying and hardening, the compressed body can be comminuted by any suitable method, in particular, using a removable hammer mill with a screen through which the comminuted material passes. The resulting material contains a certain proportion of fibrous material (from the original waste such as textiles, plastics and cellulose materials) and a certain proportion of crushed minerals (such as glass, limestone, etc. or organic matter from the waste) Subdivided material of the resulting granulated particles. The length of the fibrous material is adjusted so that most of the fiber lengths are within a given range, preferably 0.1- between 30 mm. For example, when crushing compressed bodies, the length of fibers can be adjusted by selecting a suitable fineness of the mill screen, such as 1-4 mm, and in general, the size of the subdivided materials can be adjusted.
对细分组的材料(对压缩体进行粉碎或磨碎制得)进行附聚处理制成颗粒,可以使用任何适当的方法,例如一种方法可使用转筒式和盘式附聚装置,也可结合使用这两种装置。Agglomeration of a subdivided group of materials (obtained by pulverizing or grinding compacts) into granules may be by any suitable method, e.g. one method may use drum and disc agglomerators, or Both devices can be used in combination.
在附聚处理之前,最好向细分的材料中加入至少一种粘合剂和至少一种矿物填料。Preferably at least one binder and at least one mineral filler are added to the finely divided material prior to the agglomeration treatment.
作为粘合剂,最好选用水硬水泥或清洁淤渣的锻烧灰或硅铁粉。作为矿物填料,可以使用例如碳酸钙,粉状石灰石,水硬性石灰,可使用回收建筑材料设备中的灰渣,也可使用其他工业设备中的灰渣。As a binder, hydraulic cement or calcined ash or ferrosilicon powder from cleaning sludge is preferably used. As mineral fillers, for example, calcium carbonate, powdered limestone, hydraulic lime, ashes from facilities for recycling construction materials, and ash from other industrial facilities can be used.
为了使细分的材料附聚或使细分的材料、粘合剂和最后填料的混合物附聚,最好在附聚处理之前或在附聚处理过程中向细分的材料或混合物中加入一定量的水。In order to agglomerate finely divided material or a mixture of finely divided material, binder and final filler, it is preferable to add a certain amount of water.
例如,可以以形成均匀混合物的形式向在混合器中的由粒状颗粒和纤维组成的组成的材料加入粘合剂、可能的矿物填料和水,混合器置于附聚装置之前。均匀混合物也可以在附聚处理装置里形成。作为一种选择,也可以向由粒状颗粒和纤维组成的细分的材料加入粘合剂和最后的矿物填料,在混合器(位于附聚处理装置之前)中,形成初级均匀混合物,并在附聚处理装置中加入足量的水使混合物附聚。For example, binder, possible mineral fillers and water can be added in a homogeneous mixture to the material consisting of granular particles and fibers in a mixer placed before the agglomeration device. A homogeneous mixture can also be formed in an agglomeration treatment unit. As an option, it is also possible to add binders and final mineral fillers to the subdivided material consisting of granular particles and fibers, in the mixer (located before the agglomeration treatment device), to form a primary homogeneous mixture, and in the adjacent Sufficient water is added to the polytreater to agglomerate the mixture.
根据另一个凳┍痉椒ǖ母慕桨福澈霞梁涂笪锾盍虾蜕鲜隽?的水在混合器(位于制粒装置之前)中混合,如此得到的混合物与由粒状颗粒和纤维组成的混合物同时引入制粒装置。根据另外一个改进本方法操作方案,细分的材料(由粒状颗粒和纤维组成)与粘合剂和矿物填料的均匀混合物,可以在同时用作混合器的转筒式制粒仪中制备,然后加入上述量的水使混合物附聚成颗粒形式。转筒以形成颗粒的方式运转。然后把所形成的颗粒转入板式制粒装置,在那里结束附聚处理。例如,可以向制粒装置供给粘合剂和矿物填料的均匀混合物,或者甚至是粘合剂、矿物填料和由粒状颗粒的纤维组成的细分的材料,以增大初始颗粒,并生成由一个内核和一个成分不同于内核的外壳组成的颗粒。这种特殊的处理,可以得到具有一个比内核更坚硬的外壳的颗粒。According to another stool ┍Jiaojiao: Mother Mu Paddle Fu Chexia Liang coated with 甾盍 shrimp slough fresh Jun? The water is mixed in the mixer (located before the granulation device), the mixture thus obtained is mixed with the granular granules and The mixture of fibers is simultaneously introduced into the pelletizing unit. According to another modification of the method, a homogeneous mixture of subdivided material (consisting of granular particles and fibers) with binders and mineral fillers can be prepared in a drum granulator that also serves as a mixer, and then The above amount of water was added to agglomerate the mixture into granular form. The drum operates in the form of pellets. The resulting granules are then transferred to a plate granulator where the agglomeration process ends. For example, a homogeneous mixture of binder and mineral filler, or even a finely divided material consisting of binder, mineral filler and fibers of granulated granules, can be supplied to the granulation unit to enlarge the primary granulation and produce a A particle consisting of an inner core and an outer shell of composition different from the inner core. This special treatment results in particles with an outer shell that is harder than the inner core.
最好对由附聚处理得到的颗粒作进一步的硬化处理。例如,硬化处理(其条件有赖于构成颗粒的材料的性能,主要是依赖于所用粘合剂的性能)至少包括一种操作,即对颗粒进行高压、加热或汽蒸作用,或者结合上述三种因素的两种进行作用。很明显,上述操作可同另一种操作结合,制得具有理想结构特别是复合结构的颗粒。Preferably, the particles obtained from the agglomeration treatment are subjected to a further hardening treatment. For example, hardening (the conditions of which depend on the properties of the materials constituting the particles, mainly on the properties of the binder used) includes at least one operation, that is, the application of high pressure, heat or steam to the particles, or a combination of the above three Two types of factors play a role. Obviously, the above operation can be combined with another operation to obtain particles with a desired structure, especially a composite structure.
实例1Example 1
由粉碎的或磨成粉末的生活垃圾制备952份(重量)初级均匀混合物。混合物湿度含量为30%(重量)(由从1000份重量的生活垃圾中去除48份重量的金属块所致),混合物含有50份(重量)生石灰和5份(重量)碳酸钙。混合物在具有转轴和压模的压缩机中以150巴的压力进行压缩以制成直径为8毫米和可变长度(在10-20毫米之间)的园筒形压缩体。压缩体在具有水平轴的旋转管式加热炉或窑中通过,进行干燥和硬化处理。温度为250℃的热空气流通过加热炉或窑,压缩体通过窑的时间为30分钟。952 parts by weight of a primary homogeneous mixture were prepared from comminuted or pulverized domestic waste. The moisture content of the mixture was 30% by weight (resulting from the removal of 48 parts by weight of metal lumps from 1000 parts by weight of domestic waste), and the mixture contained 50 parts by weight of quicklime and 5 parts by weight of calcium carbonate. The mixture is compressed at a pressure of 150 bar in a compressor with a rotating shaft and a die to produce a cylindrical compressed body with a diameter of 8 mm and variable length (between 10-20 mm). The compressed body passes through a rotating tubular furnace or kiln with a horizontal axis, where it is dried and hardened. The hot air flow at a temperature of 250°C passes through the heating furnace or kiln, and the time for the compressed body to pass through the kiln is 30 minutes.
以这种方式得到的压缩体为720份(重量),湿度含量略低于1%(重量)。The compact obtained in this way contained 720 parts by weight and had a moisture content of slightly less than 1% by weight.
这些压缩体在配有直径为2毫米筛网的锤式粉碎机中粉碎成细粉末,得到一种由粒状颗粒和可变长度为0.1-30毫米的纤维组成的细分的材料。These compacts are pulverized into a fine powder in a hammer mill equipped with a 2 mm diameter screen to obtain a finely divided material consisting of granulated particles and fibers with a variable length of 0.1-30 mm.
按下面比例含量(重量份),在混合器中制备细分材料、水硬水泥和白恶粉的均匀混合物。A homogeneous mixture of finely divided materials, hydraulic cement and silica powder was prepared in a mixer in the following proportions (parts by weight).
细的垃圾材料:2Fine trash material: 2
含钙岩粉末: 1Calcareous Rock Powder: 1
水硬水泥: 1Hydraulic cement: 1
将上述混合物加入一定量的水(在100份重量上述混合物中加入70份重量的水),以形成糊状物。然后转筒式混合器作为制粒筒使用,把糊状物制成球状颗粒。所得颗粒转入制粒盘。制粒盘转动时,加入等重量比的水泥和石灰粉的干燥均匀混合物(在100份初始细分的材料中加入约40份此混合物)。这样,颗粒的直径不断增大,达到所需最终直径的颗粒落到盘外,最终得到的颗粒在环境温度和正常温度的条件下,在空气中存放几天进行干燥。这样得到的颗粒直径为2-15毫米。总体密度750kg/m3,湿度含量为30%(重量)。每个颗粒都具有比其内核更硬、更不易溶于水的球形部分或球形外壳。A certain amount of water (70 parts by weight of water was added to 100 parts by weight of the above mixture) was added to the above mixture to form a paste. The tumble mixer is then used as a granulation drum to make the paste into spherical granules. The resulting granules are transferred to a granulation pan. While the granulating disc is rotating, a dry homogeneous mixture of cement and lime powder in equal weight ratios (approximately 40 parts of this mixture to 100 parts of the initially finely divided material) is added. In this way, the diameter of the granules increases continuously, the granules reaching the desired final diameter fall out of the pan, and the final granules are dried in air at ambient and normal temperature conditions for several days. The particles thus obtained have a diameter of 2-15 mm. The overall density is 750kg/m 3 and the moisture content is 30% by weight. Each particle has a spherical portion or outer shell that is harder and less water soluble than its inner core.
实例2Example 2
按实例1第一部分所述方法,把生活垃圾转变为由粒状颗粒和纤维组成的惰性、难于溶解的细分材料。然后把细分材料在制粒盘中制粒,制成一种球状颗粒形式的材料。所使用的方法与实例1方法类似,但使用的制粒盘有两个轮圈,而不是一个轮圈,亦即围绕制粒盘的中心部分有一环形区。As described in the first part of Example 1, domestic waste was converted into an inert, hardly soluble finely divided material consisting of granular particles and fibers. The finely divided material is then granulated in a granulation pan to produce a material in the form of spherical granules. The method used was similar to that of Example 1, but the pelletizing disk was used with two rims instead of one rim, ie an annular area surrounding the central part of the pelletizing disk.
加入制粒盘中心部分的初始混合物的组成如下(重量份数):The composition of the initial mixture added to the central part of the granulation disk is as follows (parts by weight):
细垃圾材料:10Fine trash material: 10
大硬水泥: 7Big Hard Cement: 7
把混合物倒入制粒盘,以向制粒盘中混合物喷洒的形式加入与实例1中相同比例量的水。通过中央圆形制粒部分的轮圈而进入环形制粒区的颗粒直径是不同的,在7-11毫米之间。在环形制粒区,把波特兰水泥和石灰质粉的均匀混合物撒在颗粒上,混合物中波特兰水泥和石灰质粉的组成如下(重量份):The mixture was poured into a granulation pan and the same proportion of water as in Example 1 was added in the form of spraying the mixture in the granulation pan. The diameter of the particles entering the annular granulation zone through the rim of the central circular granulation section is different, between 7-11 mm. In the annular granulation zone, the uniform mixture of Portland cement and lime powder is sprinkled on the particles, and the composition of Portland cement and lime powder in the mixture is as follows (parts by weight):
波特兰水泥:1Portland Cement: 1
石灰质粉: 1Lime powder: 1
所用混合物量为在100份(重量)的细分的材料(由垃圾的粒状颗粒和纤维组成)中含50份(重量),在加入混合物的同时,以喷洒形式加水进行附聚。The mixture was used in an amount of 50 parts by weight to 100 parts by weight of finely divided material (consisting of granulated particles and fibers of garbage), agglomerated by spraying water while adding the mixture.
最后得到的直径在8-12毫米之间的颗粒,越过环形制粒区的外轮圈,暴露在环境温度下(在正常湿度下)以进行最后硬化。The resulting pellets, with a diameter between 8 and 12 mm, pass over the outer rim of the annular granulation zone and are exposed to ambient temperature (at normal humidity) for final hardening.
这样可以得到外壳比中心部分更硬的颗粒,材料的总体密度在700kg/m3范围。This results in pellets with a harder outer shell than the central part, with an overall density of material in the range of 700kg/ m3 .
实例3Example 3
按照实例1所述方法得到的颗粒,用作水泥制备中的集料。为这一目的,将颗粒与水泥和水的稀砂浆混合,相当于每立方米的水泥和颗粒混合物中水泥量为400公斤,水/水泥重量比为0.57。The granules obtained as described in Example 1 were used as aggregate in the preparation of cement. For this purpose, the granules were mixed with a dilute mortar of cement and water corresponding to an amount of cement of 400 kg per cubic meter of cement and granule mixture, with a water/cement weight ratio of 0.57.
经过36天的硬化后,得到的混凝土块密度为1500kg/m3,机械性能如下:After 36 days of hardening, the resulting concrete block has a density of 1500kg/m 3 and mechanical properties as follows:
弯曲牵引为N/mm2:1.78Bending traction is N/mm 2 : 1.78
抗压力(立方)N/mm2:7.17Compression resistance (cubic) N/mm 2 : 7.17
绝热系数w/m.k: 0.55Thermal insulation coefficient w/m.k: 0.55
实例4Example 4
按照实例1所述方法制得的颗粒与水泥混合,加水,混合物在模子中振动压缩制备砖,水泥用量是每立方米混合物300公斤。在环境温度下,经过32天干燥硬化,使水的含量(重量)约相对水泥重量的20%,所得的砖比重为1650kg/m3,抗压力为4.3N/mm2,绝热系数为0.45w/m.k,可用于建筑具有很好绝热性能的墙壁。The granule prepared according to the method described in Example 1 is mixed with cement, water is added, and the mixture is vibrated and compressed in a mold to prepare bricks. The cement consumption is 300 kilograms per cubic meter of mixture. At ambient temperature, after 32 days of drying and hardening, the water content (weight) is about 20% relative to the weight of the cement. The specific gravity of the obtained brick is 1650kg/m 3 , the compression resistance is 4.3N/mm 2 , and the thermal insulation coefficient is 0.45w /mk, can be used to build walls with good thermal insulation properties.
Claims (18)
Applications Claiming Priority (2)
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| CH4282/87A CH673454A5 (en) | 1987-11-02 | 1987-11-02 | |
| CH4282/87-0 | 1987-11-02 |
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| CN1034148A true CN1034148A (en) | 1989-07-26 |
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| CN88107505A Pending CN1034148A (en) | 1987-11-02 | 1988-11-01 | Rubbish is transformed into a kind of method of grain shape material |
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| JP (1) | JPH01151983A (en) |
| KR (1) | KR890007802A (en) |
| CN (1) | CN1034148A (en) |
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| BR (1) | BR8805574A (en) |
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| GB (1) | GB2211836A (en) |
| GR (1) | GR1000351B (en) |
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| IT (1) | IT1223844B (en) |
| JO (1) | JO1546B1 (en) |
| MA (1) | MA21420A1 (en) |
| MC (1) | MC1980A1 (en) |
| NL (1) | NL8802491A (en) |
| NO (1) | NO884866L (en) |
| OA (1) | OA08964A (en) |
| PL (1) | PL275554A1 (en) |
| PT (1) | PT88814A (en) |
| SE (1) | SE8803844L (en) |
| TN (1) | TNSN88112A1 (en) |
| YU (1) | YU199988A (en) |
| ZA (1) | ZA888201B (en) |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
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| CN1068251C (en) * | 1998-07-16 | 2001-07-11 | 北京博朗环保技术开发公司 | Garbage treatment technology with no harm, no residuals, easy to separate and realize reutilization |
| CN1070147C (en) * | 1997-09-08 | 2001-08-29 | 曹荣华 | Method and device for complex processing house-hold refuse |
| CN1093437C (en) * | 1998-08-07 | 2002-10-30 | 北京清华紫光泰和通环保技术有限公司 | City domestic refuse treating method |
| CN1108201C (en) * | 1998-08-07 | 2003-05-14 | 浙江大学 | Method for baking light bricks using sludge heat energy |
| CN110681310A (en) * | 2019-09-02 | 2020-01-14 | 深圳市为海建材有限公司 | Granulation equipment and method for preparing residual sludge soil particles |
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| WO1990015205A1 (en) * | 1989-06-07 | 1990-12-13 | Danielsen, Marit, Helene | Building element |
| IT1235772B (en) * | 1989-06-09 | 1992-09-28 | Master Srl | PROCEDURE FOR THE REUSE OF SOLID WASTE MATERIALS, USING THERMOPLASTIC RESIN |
| ES2036480B1 (en) * | 1991-11-08 | 1993-12-16 | Sibersa | PROCEDURE FOR MANUFACTURING A SOLID COMBUSTIBLE MATERIAL FROM URBAN AND / OR INDUSTRIAL AND / OR AGRICULTURAL ASSIMILABLE SOLID WASTE. |
| DE4336613C1 (en) * | 1993-10-27 | 1995-02-09 | Bayer Ag | Process for colouring building materials |
| DE4343080A1 (en) * | 1993-12-16 | 1995-06-29 | Philipp Stephanie | Conversion of organic substances, residues, waste to mineralized raw materials as base material |
| DE4434433C1 (en) | 1994-09-27 | 1995-12-21 | Werner Ratjen | Working up waste material for recycling |
| DE29505314U1 (en) * | 1995-03-29 | 1995-06-01 | Döcke, Wolfgang, 06484 Quedlinburg | Building material from waste materials |
| AU667659B3 (en) * | 1995-06-19 | 1996-03-28 | Petemic Technology Pty Ltd | A waste recycling process and apparatus |
| FR2882277B1 (en) * | 2005-02-23 | 2007-09-14 | Marc Gombart | USE AND METHOD OF NODULIZATION TO FACILITATE PACKAGING, HANDLING, TREATMENT AND / OR HOLD IN TASTE OF WET, GENERALLY PASTY AND / OR COLLANT WASTE OBTAINED FROM SLUDGE |
| DE102016217367A1 (en) | 2016-09-13 | 2018-03-15 | Robert Bosch Gmbh | A method for producing an active material for an electrode of a battery cell, an arrangement for producing an active material for an electrode of a battery cell and battery cell |
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| JPS4899964A (en) * | 1972-03-31 | 1973-12-17 | ||
| DE2322655C2 (en) * | 1973-05-03 | 1984-06-20 | Schering AG, 1000 Berlin und 4709 Bergkamen | Prostaglandin F? 2???? Esters, process for their preparation and their use for the purification of prostaglandin F? 2???? |
| ES415447A1 (en) * | 1973-06-01 | 1976-02-16 | Schrader Voss | Procedure for the elimination by transformation of solid waste materials. (Machine-translation by Google Translate, not legally binding) |
| DE2432606A1 (en) * | 1974-07-06 | 1976-01-22 | Helvisol Ag | PROCESS FOR THE MANUFACTURING OF ASBESTOS-LIKE, NON-COMBUSTIBLE SUBSTANCES FROM MUELL |
| FR2286116A1 (en) * | 1974-09-26 | 1976-04-23 | Ponnier Andre | Aggregates useful as gravel substitutes for concrete - and prepd. from household refuse powdered and mixed with silicates and binders |
| FR2472421A1 (en) * | 1979-03-13 | 1981-07-03 | Geronimo Hilaire | Transforming garbage contg. cellulose into useful products - by reaction with calcium cpd., and agglomerating the reaction product |
| DE3128560C1 (en) * | 1981-07-18 | 1983-02-24 | Mannesmann Veba Umwelttechnik GmbH, 4690 Herne | Process for the preparation of the combustible fraction of household waste to be briquetted and plant for carrying out the process |
| EP0139791A1 (en) * | 1983-09-06 | 1985-05-08 | Bryce B. Wilde | Building material and method of manufacturing same |
| CH665785A5 (en) * | 1985-06-19 | 1988-06-15 | Loma Finance Inc | PROCESS FOR THE CONVERSION OF ORGANIC AND MINERAL WASTE INTO SOLID, INERT AND INSOLUBLE MATERIAL IN WATER. |
| DE3525111A1 (en) * | 1985-07-13 | 1987-01-15 | Hubert Eirich | METHOD FOR PRODUCING LEAK-OUT AGGLOMERATES |
| JPS6291285A (en) * | 1985-10-15 | 1987-04-25 | Seiji Motoki | Method for treating waste |
| CH672309A5 (en) * | 1987-03-19 | 1989-11-15 | Catrel Sa |
-
1987
- 1987-11-02 CH CH4282/87A patent/CH673454A5/fr not_active IP Right Cessation
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1988
- 1988-09-19 FR FR8812181A patent/FR2622483A1/en active Pending
- 1988-09-21 IT IT6784188A patent/IT1223844B/en active
- 1988-09-27 DE DE3832771A patent/DE3832771A1/en not_active Withdrawn
- 1988-09-29 ES ES8802950A patent/ES2008610A6/en not_active Expired
- 1988-09-30 IL IL87895A patent/IL87895A0/en unknown
- 1988-10-04 GR GR880100655A patent/GR1000351B/en unknown
- 1988-10-11 NL NL8802491A patent/NL8802491A/en not_active Application Discontinuation
- 1988-10-13 MC MC882011A patent/MC1980A1/en unknown
- 1988-10-17 AU AU23904/88A patent/AU2390488A/en not_active Abandoned
- 1988-10-20 PT PT8881488A patent/PT88814A/en unknown
- 1988-10-25 GB GB8824980A patent/GB2211836A/en not_active Withdrawn
- 1988-10-26 YU YU199988A patent/YU199988A/en unknown
- 1988-10-27 BR BR8805574A patent/BR8805574A/en unknown
- 1988-10-27 SE SE8803844A patent/SE8803844L/en not_active Application Discontinuation
- 1988-10-27 MA MA21661A patent/MA21420A1/en unknown
- 1988-10-28 PL PL27555488A patent/PL275554A1/en unknown
- 1988-10-31 DD DD88321269A patent/DD283342A5/en not_active IP Right Cessation
- 1988-11-01 FI FI885008A patent/FI885008A7/en not_active Application Discontinuation
- 1988-11-01 CN CN88107505A patent/CN1034148A/en active Pending
- 1988-11-01 DK DK608188A patent/DK608188A/en not_active Application Discontinuation
- 1988-11-01 NO NO88884866A patent/NO884866L/en unknown
- 1988-11-01 JO JO19881546A patent/JO1546B1/en active
- 1988-11-02 ZA ZA888201A patent/ZA888201B/en unknown
- 1988-11-02 KR KR1019880014429A patent/KR890007802A/en not_active Withdrawn
- 1988-11-02 TN TNSN88112 patent/TNSN88112A1/en unknown
- 1988-11-02 OA OA59458A patent/OA08964A/en unknown
- 1988-11-02 JP JP63278490A patent/JPH01151983A/en active Pending
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1070147C (en) * | 1997-09-08 | 2001-08-29 | 曹荣华 | Method and device for complex processing house-hold refuse |
| CN1068251C (en) * | 1998-07-16 | 2001-07-11 | 北京博朗环保技术开发公司 | Garbage treatment technology with no harm, no residuals, easy to separate and realize reutilization |
| CN1093437C (en) * | 1998-08-07 | 2002-10-30 | 北京清华紫光泰和通环保技术有限公司 | City domestic refuse treating method |
| CN1108201C (en) * | 1998-08-07 | 2003-05-14 | 浙江大学 | Method for baking light bricks using sludge heat energy |
| CN110681310A (en) * | 2019-09-02 | 2020-01-14 | 深圳市为海建材有限公司 | Granulation equipment and method for preparing residual sludge soil particles |
Also Published As
| Publication number | Publication date |
|---|---|
| FI885008L (en) | 1989-05-03 |
| JO1546B1 (en) | 1989-01-25 |
| IL87895A0 (en) | 1989-03-31 |
| TNSN88112A1 (en) | 1990-07-10 |
| MA21420A1 (en) | 1989-07-01 |
| NL8802491A (en) | 1989-06-01 |
| BR8805574A (en) | 1989-07-11 |
| FI885008A0 (en) | 1988-11-01 |
| FI885008A7 (en) | 1989-05-03 |
| PL275554A1 (en) | 1989-07-10 |
| CH673454A5 (en) | 1990-03-15 |
| DK608188D0 (en) | 1988-11-01 |
| SE8803844L (en) | 1989-05-03 |
| DK608188A (en) | 1989-05-03 |
| JPH01151983A (en) | 1989-06-14 |
| FR2622483A1 (en) | 1989-05-05 |
| AU2390488A (en) | 1989-05-04 |
| GR1000351B (en) | 1992-06-25 |
| DD283342A5 (en) | 1990-10-10 |
| OA08964A (en) | 1990-11-30 |
| DE3832771A1 (en) | 1989-05-11 |
| PT88814A (en) | 1989-09-14 |
| GB8824980D0 (en) | 1988-11-30 |
| NO884866D0 (en) | 1988-11-01 |
| ES2008610A6 (en) | 1989-07-16 |
| YU199988A (en) | 1990-02-28 |
| KR890007802A (en) | 1989-05-07 |
| IT8867841A0 (en) | 1988-09-21 |
| NO884866L (en) | 1989-05-03 |
| ZA888201B (en) | 1989-07-26 |
| IT1223844B (en) | 1990-09-29 |
| MC1980A1 (en) | 1989-11-23 |
| GB2211836A (en) | 1989-07-12 |
| SE8803844D0 (en) | 1988-10-27 |
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