CN211445482U - Ceramic sludge treatment system - Google Patents
Ceramic sludge treatment system Download PDFInfo
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- CN211445482U CN211445482U CN202021524685.7U CN202021524685U CN211445482U CN 211445482 U CN211445482 U CN 211445482U CN 202021524685 U CN202021524685 U CN 202021524685U CN 211445482 U CN211445482 U CN 211445482U
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- 239000000919 ceramic Substances 0.000 title claims abstract description 115
- 239000010802 sludge Substances 0.000 title claims abstract description 115
- 230000007246 mechanism Effects 0.000 claims abstract description 44
- 238000001035 drying Methods 0.000 claims abstract description 33
- 238000005189 flocculation Methods 0.000 claims abstract description 31
- 230000016615 flocculation Effects 0.000 claims abstract description 31
- 230000018044 dehydration Effects 0.000 claims abstract description 22
- 238000006297 dehydration reaction Methods 0.000 claims abstract description 22
- 238000002156 mixing Methods 0.000 claims abstract description 19
- 238000003756 stirring Methods 0.000 claims abstract description 19
- 239000000843 powder Substances 0.000 claims abstract description 18
- 239000007800 oxidant agent Substances 0.000 claims abstract description 14
- 230000001590 oxidative effect Effects 0.000 claims abstract description 11
- 239000003814 drug Substances 0.000 claims description 9
- 238000007873 sieving Methods 0.000 claims description 9
- 239000002184 metal Substances 0.000 claims description 6
- 238000010298 pulverizing process Methods 0.000 claims description 6
- 229940079593 drug Drugs 0.000 claims description 3
- 230000005540 biological transmission Effects 0.000 claims description 2
- 239000008394 flocculating agent Substances 0.000 claims description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 18
- 239000002245 particle Substances 0.000 abstract description 16
- 238000012216 screening Methods 0.000 abstract description 13
- 238000000034 method Methods 0.000 abstract description 8
- 239000004566 building material Substances 0.000 abstract description 6
- 239000006185 dispersion Substances 0.000 abstract description 4
- 230000004048 modification Effects 0.000 abstract description 2
- 238000012986 modification Methods 0.000 abstract description 2
- 208000005156 Dehydration Diseases 0.000 description 20
- 230000000694 effects Effects 0.000 description 9
- 239000010410 layer Substances 0.000 description 9
- 239000004567 concrete Substances 0.000 description 5
- 238000004519 manufacturing process Methods 0.000 description 4
- 238000009413 insulation Methods 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 229920000642 polymer Polymers 0.000 description 3
- 230000005855 radiation Effects 0.000 description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- 230000015556 catabolic process Effects 0.000 description 2
- 239000004568 cement Substances 0.000 description 2
- 238000012668 chain scission Methods 0.000 description 2
- 238000006731 degradation reaction Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000001704 evaporation Methods 0.000 description 2
- 239000010419 fine particle Substances 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 238000005498 polishing Methods 0.000 description 2
- 230000008929 regeneration Effects 0.000 description 2
- 238000011069 regeneration method Methods 0.000 description 2
- 239000013049 sediment Substances 0.000 description 2
- 239000011358 absorbing material Substances 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 230000006378 damage Effects 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 238000007602 hot air drying Methods 0.000 description 1
- 238000007517 polishing process Methods 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 238000000197 pyrolysis Methods 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- HBMJWWWQQXIZIP-UHFFFAOYSA-N silicon carbide Chemical compound [Si+]#[C-] HBMJWWWQQXIZIP-UHFFFAOYSA-N 0.000 description 1
- 229910010271 silicon carbide Inorganic materials 0.000 description 1
- 235000012239 silicon dioxide Nutrition 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 239000002344 surface layer Substances 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
- 239000002918 waste heat Substances 0.000 description 1
- -1 when standing Substances 0.000 description 1
Images
Classifications
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B02—CRUSHING, PULVERISING, OR DISINTEGRATING; PREPARATORY TREATMENT OF GRAIN FOR MILLING
- B02C—CRUSHING, PULVERISING, OR DISINTEGRATING IN GENERAL; MILLING GRAIN
- B02C18/00—Disintegrating by knives or other cutting or tearing members which chop material into fragments
- B02C18/06—Disintegrating by knives or other cutting or tearing members which chop material into fragments with rotating knives
- B02C18/14—Disintegrating by knives or other cutting or tearing members which chop material into fragments with rotating knives within horizontal containers
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B02—CRUSHING, PULVERISING, OR DISINTEGRATING; PREPARATORY TREATMENT OF GRAIN FOR MILLING
- B02C—CRUSHING, PULVERISING, OR DISINTEGRATING IN GENERAL; MILLING GRAIN
- B02C23/00—Auxiliary methods or auxiliary devices or accessories specially adapted for crushing or disintegrating not provided for in preceding groups or not specially adapted to apparatus covered by a single preceding group
- B02C23/08—Separating or sorting of material, associated with crushing or disintegrating
- B02C23/16—Separating or sorting of material, associated with crushing or disintegrating with separator defining termination of crushing or disintegrating zone, e.g. screen denying egress of oversize material
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B07—SEPARATING SOLIDS FROM SOLIDS; SORTING
- B07B—SEPARATING SOLIDS FROM SOLIDS BY SIEVING, SCREENING, SIFTING OR BY USING GAS CURRENTS; SEPARATING BY OTHER DRY METHODS APPLICABLE TO BULK MATERIAL, e.g. LOOSE ARTICLES FIT TO BE HANDLED LIKE BULK MATERIAL
- B07B1/00—Sieving, screening, sifting, or sorting solid materials using networks, gratings, grids, or the like
- B07B1/28—Moving screens not otherwise provided for, e.g. swinging, reciprocating, rocking, tilting or wobbling screens
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/06—Treatment of sludge; Devices therefor by oxidation
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/13—Treatment of sludge; Devices therefor by de-watering, drying or thickening by heating
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/13—Treatment of sludge; Devices therefor by de-watering, drying or thickening by heating
- C02F11/131—Treatment of sludge; Devices therefor by de-watering, drying or thickening by heating using electromagnetic or ultrasonic waves
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/14—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
- C02F11/147—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents using organic substances
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- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Hydrology & Water Resources (AREA)
- Life Sciences & Earth Sciences (AREA)
- Mechanical Engineering (AREA)
- Food Science & Technology (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Physics & Mathematics (AREA)
- Electromagnetism (AREA)
- Treatment Of Sludge (AREA)
Abstract
本实用新型公开了一种陶瓷污泥处理系统,所述系统还包括按照污泥处理顺序依次设置的粉碎过筛装置、搅拌混合装置、干燥装置,所述粉碎过筛装置用于将脱水后的陶瓷污泥块进行粉碎、过筛,所述搅拌混合装置设有干粉加料机构,所述干粉加料机构用于向粉碎后的陶瓷污泥中加入氧化剂干粉,所述干燥装置包括超声波发生机构和微波发生器,所述干燥装置用于去除陶瓷污泥中的水分和破坏絮凝剂。本实用新型提供的陶瓷污泥处理系统,能实现对陶瓷污泥进行絮凝脱水、分散、干化、表面改性等多个工艺步骤,处理后的陶瓷污泥变为分散的陶瓷微粉颗粒,含水率低,可以直接用于制建材利用。
The utility model discloses a ceramic sludge treatment system. The system further comprises a crushing and screening device, a stirring and mixing device and a drying device, which are arranged in sequence according to the sludge treatment sequence. The ceramic sludge block is crushed and sieved. The stirring and mixing device is provided with a dry powder feeding mechanism. The dry powder feeding mechanism is used to add oxidant dry powder to the crushed ceramic sludge. The drying device includes an ultrasonic generating mechanism and a microwave. Generator, the drying device is used to remove the moisture in the ceramic sludge and destroy the flocculant. The ceramic sludge treatment system provided by the utility model can realize multiple process steps such as flocculation and dehydration, dispersion, drying and surface modification of the ceramic sludge, and the treated ceramic sludge becomes dispersed ceramic fine powder particles containing water. The rate is low and can be directly used for making building materials.
Description
技术领域technical field
本实用新型涉及污泥处理技术领域,特别涉及一种陶瓷污泥处理系统。The utility model relates to the technical field of sludge treatment, in particular to a ceramic sludge treatment system.
背景技术Background technique
陶瓷污泥是陶瓷生产过程中抛光工艺环节产生的污泥,其主要成分是陶瓷微粉、助研剂和水的混合物,其中的陶瓷微粉主要成分是二氧化硅和碳化硅,陶瓷污泥中的陶瓷微粉具有粒径小、硬度大的特点,经处理后的陶瓷污泥,可用作建筑材料的细骨料,或者做成高品质透水砌块的面层材料。但是,现有技术中,由于处理工艺的限制,陶瓷抛光污泥通常经絮凝、脱水、干燥后,直接进行填埋,利用价值较低。也有人尝试将其作为建筑材料,如用于制作混凝土砌块。但由于陶瓷抛光污泥处理工艺的落后,使得处理后的陶瓷污泥容易板结,含水率高,且存在絮凝剂,这样的陶瓷污泥用作建筑材料时,存在以下缺陷:1、由于处理后的陶瓷污泥含水率仍然接近40%,当将其用于制作砌块时,陶瓷污泥中的水分会增加混凝土的水灰比,导致砌块强度偏低;2、大块的板结陶瓷污泥直接用于制建材时,块状的污泥会在建材内部形成力学薄弱点,导致砌块强度偏低;3、脱水后的陶瓷污泥中存在高分子絮凝剂,其会对水泥的水化产生不利影响,使得混凝土砌块的早期强度差,最终影响混凝土制品的力学性能。Ceramic sludge is the sludge produced in the polishing process in the ceramic production process. Its main components are a mixture of ceramic micropowder, grinding aid and water. The main components of ceramic micropowder are silicon dioxide and silicon carbide. Ceramic micropowder has the characteristics of small particle size and high hardness. The treated ceramic sludge can be used as a fine aggregate for building materials, or as a surface layer material for high-quality permeable blocks. However, in the prior art, due to the limitation of the treatment process, the ceramic polishing sludge is usually directly landfilled after flocculation, dehydration and drying, and the utilization value is low. There are also attempts to use it as a building material, such as for making concrete blocks. However, due to the backwardness of the ceramic polishing sludge treatment process, the treated ceramic sludge is easy to harden, the water content is high, and there is a flocculant. When such ceramic sludge is used as a building material, there are the following defects: 1. The moisture content of the ceramic sludge is still close to 40%. When it is used to make blocks, the water in the ceramic sludge will increase the water-cement ratio of the concrete, resulting in a low block strength; 2. Large pieces of compacted ceramic sludge When the mud is directly used to make building materials, the lumpy sludge will form mechanical weak points inside the building materials, resulting in low block strength; 3. There are polymer flocculants in the dehydrated ceramic sludge, which will affect the water content of the cement. It has an adverse effect on the formation of concrete blocks, which makes the early strength of concrete blocks poor, and ultimately affects the mechanical properties of concrete products.
可见,现有技术还有待改进和提高。It can be seen that the existing technology still needs to be improved and improved.
实用新型内容Utility model content
鉴于上述现有技术的不足之处,本实用新型提供一种陶瓷污泥处理系统,旨在提高陶瓷污泥的处理效果,提升陶瓷污泥的再生利用价值。In view of the above-mentioned deficiencies of the prior art, the present invention provides a ceramic sludge treatment system, which aims to improve the treatment effect of the ceramic sludge and enhance the regeneration and utilization value of the ceramic sludge.
为了达到上述目的,本实用新型采取了以下技术方案:In order to achieve the above object, the utility model has adopted the following technical solutions:
一种陶瓷污泥处理系统,所述系统包括絮凝装置和脱水装置,其中,所述系统还包括按照污泥处理顺序依次设置的粉碎过筛装置、搅拌混合装置、干燥装置,所述粉碎过筛装置用于将脱水后的陶瓷污泥块进行粉碎、过筛,所述搅拌混合装置设有干粉加料机构,所述干粉加料机构用于向粉碎后的陶瓷污泥中加入氧化剂干粉,所述干燥装置包括超声波发生机构和微波发生器,所述干燥装置用于去除陶瓷污泥中的水分和破坏絮凝剂。A ceramic sludge treatment system, the system includes a flocculation device and a dehydration device, wherein the system further includes a crushing and screening device, a stirring and mixing device, and a drying device arranged in sequence according to the sludge treatment sequence, the crushing and screening device. The device is used to pulverize and sieve the dehydrated ceramic sludge block. The stirring and mixing device is provided with a dry powder feeding mechanism, and the dry powder feeding mechanism is used to add oxidant dry powder to the pulverized ceramic sludge. The device includes an ultrasonic generating mechanism and a microwave generator, and the drying device is used for removing moisture in the ceramic sludge and destroying the flocculant.
所述陶瓷污泥处理系统中,所述干燥装置包括密封的输送通道,所述超声波发生机构包括超声波发生器和超声波换能器,所述输送通道的底部设有输送带,输送通道的内侧壁上布有若干个超声波换能器和若干个微波发生器,输送通道外设有超声波发生器,所述超声波发生器与超声波换能器电性连接。In the ceramic sludge treatment system, the drying device includes a sealed conveying channel, the ultrasonic generating mechanism includes an ultrasonic generator and an ultrasonic transducer, a conveying belt is arranged at the bottom of the conveying channel, and the inner wall of the conveying channel is Several ultrasonic transducers and several microwave generators are arranged on the upper part, and an ultrasonic generator is arranged outside the conveying channel, and the ultrasonic generator is electrically connected with the ultrasonic transducer.
所述陶瓷污泥处理系统中,以输送带运动的方向为后方,所述超声波换能器均布于输送通道前2/3段的侧壁上,所述微波发生器均布于输送通道后2/3段的侧壁段上。In the ceramic sludge treatment system, the direction of movement of the conveyor belt is the rear, the ultrasonic transducers are evenly distributed on the side walls of the front 2/3 of the conveying channel, and the microwave generators are evenly distributed behind the conveying channel. 2/3 of the side wall section.
所述陶瓷污泥处理系统中,所述输送通道的后端设有热风入口,输送通道的前端设有热风出口,所述热风入口和热风出口均设有金属网,用于防止微波泄漏。In the ceramic sludge treatment system, the rear end of the conveying channel is provided with a hot air inlet, the front end of the conveying channel is provided with a hot air outlet, and both the hot air inlet and the hot air outlet are provided with metal meshes to prevent microwave leakage.
所述陶瓷污泥处理系统中,所述输送通道的内壁设有微波屏蔽层和隔音层。In the ceramic sludge treatment system, the inner wall of the conveying channel is provided with a microwave shielding layer and a sound insulation layer.
所述陶瓷污泥处理系统中,所述絮凝装置包括絮凝槽,絮凝槽底部为锥形结构,絮凝槽上方设有加药机构。In the ceramic sludge treatment system, the flocculation device includes a flocculation tank, the bottom of the flocculation tank is a conical structure, and a dosing mechanism is arranged above the flocculation tank.
所述陶瓷污泥处理系统中,所述加药机构包括储药罐和设置于储药罐下方的加药泵。In the ceramic sludge treatment system, the medicine dosing mechanism includes a medicine storage tank and a medicine addition pump arranged below the medicine storage tank.
所述陶瓷污泥处理系统中,所述粉碎过筛装置包括机身以及设置在机身内的粉碎机构和过筛机构,所述过筛机构设置于粉碎机构的下方,所述过筛机构包括振动筛网。In the ceramic sludge treatment system, the crushing and screening device includes a body and a crushing mechanism and a screening mechanism arranged in the body, the screening mechanism is arranged below the crushing mechanism, and the screening mechanism includes: Vibrating screen.
所述陶瓷污泥处理系统中,所述粉碎机构包括刀片、转轴、驱动电机,所述刀片固定连接转轴,所述转轴与驱动电机传动连接。In the ceramic sludge treatment system, the pulverizing mechanism includes a blade, a rotating shaft, and a driving motor, the blade is fixedly connected to the rotating shaft, and the rotating shaft is drivingly connected to the driving motor.
所述陶瓷污泥处理系统中,所述系统还设有控制机构,所述控制机构分别与絮凝装置、脱水装置、粉碎过筛装置、搅拌混合装置、干燥装置电性连接。In the ceramic sludge treatment system, the system is further provided with a control mechanism, and the control mechanism is respectively electrically connected with the flocculation device, the dehydration device, the crushing and screening device, the stirring and mixing device, and the drying device.
有益效果:Beneficial effects:
本实用新型提供了一种陶瓷污泥处理系统,所述系统通过设置絮凝装置、脱水装置、粉碎过筛装置、搅拌混合装置、干燥装置,实现对陶瓷污泥进行絮凝脱水、分散、干化、表面改性等多个工艺步骤。所述系统能够对陶瓷污泥进行深度脱水,并且破坏陶瓷污泥内部的絮凝剂分子链,处理后的陶瓷污泥为分散的陶瓷微粉,含水率低,再生利用价值高。The utility model provides a ceramic sludge treatment system. The system is provided with a flocculation device, a dehydration device, a crushing and screening device, a stirring and mixing device, and a drying device, so as to realize flocculation, dehydration, dispersion, drying, and drying of ceramic sludge. Surface modification and other process steps. The system can deeply dewater the ceramic sludge and destroy the flocculant molecular chain inside the ceramic sludge. The treated ceramic sludge is a dispersed ceramic micropowder with low moisture content and high regeneration value.
附图说明Description of drawings
图1为本实用新型提供的陶瓷污泥处理系统的结构示意图;Fig. 1 is the structural representation of the ceramic sludge treatment system provided by the utility model;
图2为絮凝装置的结构示意图;Fig. 2 is the structural representation of flocculation device;
图3为粉碎过筛装置的结构示意图;Fig. 3 is the structural representation of crushing and sieving device;
图4为搅拌混合装置的结构示意图;Fig. 4 is the structural representation of stirring and mixing device;
图5为干燥装置的结构示意图;5 is a schematic structural diagram of a drying device;
图6为输送通道壳体的截面图;Figure 6 is a cross-sectional view of the delivery channel housing;
图7为一种优选的干燥装置的结构示意图。FIG. 7 is a schematic structural diagram of a preferred drying device.
具体实施方式Detailed ways
本实用新型提供一种陶瓷污泥处理系统,为使本实用新型的目的、技术方案及效果更加清楚、明确,以下参照附图并举实施例对本实用新型作进一步详细说明。应当理解,此处所描述的具体实施例仅用以解释本实用新型,并不用于限定本实用新型。The present utility model provides a ceramic sludge treatment system. In order to make the purpose, technical scheme and effect of the present utility model clearer and clearer, the present utility model will be further described in detail below with reference to the accompanying drawings and examples. It should be understood that the specific embodiments described herein are only used to explain the present invention, and are not used to limit the present invention.
请参阅图1-5,本实用新型提供一种陶瓷污泥处理系统,所述系统包括絮凝装置1、脱水装置2、粉碎过筛装置3、搅拌混合装置4、干燥装置5,用于完成陶瓷污泥的处理工艺步骤,所述陶瓷污泥的处理工艺包括以下步骤:(1)陶瓷污泥的絮凝沉淀,通过添加絮凝剂,使悬浮的陶瓷污泥絮凝沉淀,加速陶瓷污泥与水分离;(2)陶瓷污泥脱水,将絮凝沉淀后的陶瓷污泥脱水至30%-40%含水率;(3)脱水后的陶瓷污泥粉碎,通过粉碎机和过筛机,将脱水后的陶瓷污泥块粉碎成细颗粒;(4)添加氧化剂干粉,并通过搅拌混合,将氧化剂干粉与颗粒状的陶瓷污泥混合;(5)絮凝剂的断链和水分的去除,通过超声波、微波、热风及氧化剂的共同作用,破坏絮凝剂的长链分子。通过热风和微波内部热效应,使陶瓷污泥内部水分蒸发,得到颗粒细小,分散性好的陶瓷微粉。1-5, the present utility model provides a ceramic sludge treatment system, which includes a
如图2所示,所述絮凝装置包括絮凝槽1.1,絮凝槽1.1的侧壁上设有进料口A1.2,所述陶瓷污泥通过进料口进入絮凝槽中,絮凝槽1.1的底部为锥形结构,在锥形的底部设有出料口A1.3,在絮凝槽上方靠近进料口A1.2的位置设有加药机构,所述加药机构包括储药罐1.4和加药泵1.5,所述加药泵1.5为计量泵,所述絮凝槽还设有搅拌器A1.6,所述搅拌器A1.6用于将陶瓷污泥与絮凝剂更充分的混合。工作时,陶瓷污泥通过进料口A1.2进入絮凝槽1.1中,在进料的同时,通过加药机构加入絮凝剂,在搅拌器A1.6的搅拌混合下,絮凝剂将陶瓷污泥包覆沉淀,静置时,沉淀在絮凝槽的底部,然后从出料口A1.3流出。需要说明的是,搅拌器A1.6为间隙工作模式,加药时进行搅拌,当加药完成后停止工作,使陶瓷污泥充分沉淀。As shown in Figure 2, the flocculation device includes a flocculation tank 1.1. A feed port A1.2 is provided on the side wall of the flocculation tank 1.1. The ceramic sludge enters the flocculation tank through the feed port. The bottom of the flocculation tank 1.1 It is a conical structure, a discharge port A1.3 is arranged at the bottom of the cone, and a dosing mechanism is provided above the flocculation tank near the feeding port A1.2. The dosing mechanism includes a drug storage tank 1.4 and a feeding The medicine pump 1.5, the medicine dosing pump 1.5 is a metering pump, and the flocculation tank is also provided with an agitator A1.6, which is used to more fully mix the ceramic sludge and the flocculant. During operation, the ceramic sludge enters the flocculation tank 1.1 through the feeding port A1.2. At the same time of feeding, the flocculant is added through the dosing mechanism. The coating sediment, when standing, sediments at the bottom of the flocculation tank, and then flows out from the discharge port A1.3. It should be noted that the agitator A1.6 is in the gap working mode, stirring is performed during the dosing, and stops when the dosing is completed, so that the ceramic sludge is fully precipitated.
具体的,所述脱水装置2包括板框式脱水装置和叠螺式脱水装置,两者均可以实现对污泥进行初步脱水,除去污泥中大量的孔隙水,方便后续干燥处理。由于板框式脱水装置和叠螺式脱水装置均为现有技术,在此不做详细说明。优选的,所述脱水装置为板框式脱水装置,脱水后的陶瓷污泥水分含量可降至40%左右,便于后续的干燥处理。Specifically, the dehydration device 2 includes a plate and frame type dehydration device and a stacked screw type dehydration device, both of which can achieve preliminary dehydration of the sludge, remove a large amount of pore water in the sludge, and facilitate subsequent drying treatment. Since both the plate and frame type dehydration device and the stacked screw type dehydration device are in the prior art, they will not be described in detail here. Preferably, the dehydration device is a plate-and-frame dehydration device, and the moisture content of the dehydrated ceramic sludge can be reduced to about 40%, which is convenient for subsequent drying treatment.
具体的,如图3所示,在上述陶瓷污泥处理系统中,所述粉碎过筛装置3包括机身3.1,所述机身上设有料斗3.2,机身内设有粉碎机构和过筛机构,所述粉碎机构包括设置在机身内的刀片3.3、转轴3.4,和设置在机身外的驱动电机3.5,所述刀片3.3连接在转轴3.4上,所述转轴3.4与驱动电机3.5传动连接,所述过筛机构设置于粉碎机构的下方,包括振动筛网3.6,所述机身还设有粉料出口3.7,经振动筛网3.6筛分后的小颗粒陶瓷污泥,由粉料出口流出。由于从板框式脱水机出来的陶瓷污泥在脱水时形成了板块结构,不利于后续的进一步脱水处理和除絮凝剂处理,设置的粉碎过筛装置,主要用于将脱水后的陶瓷污泥块进行粉碎、过筛,从而提高后续脱水的效率,也便于与氧化剂混合。Specifically, as shown in FIG. 3, in the above-mentioned ceramic sludge treatment system, the crushing and
具体的,如图4所示所述搅拌混合装置4包括壳体4.1,壳体4.1的上方设有进料口B4.2,所述进料口B4.2通过输送带A(未画出)与粉碎过筛装置3的粉料出口3.7连通,壳体4.1内设有搅拌器B4.4,壳体4.1的顶部设有干粉加料机构,所述干粉加料机构包括储料罐4.5及设置在储料罐底部的开关阀A4.6,壳体的底部还设有出料口B4.7,所述出料口B4.7设有开关阀B4.8,搅拌混合时,所述开关阀B4.8是闭合的,搅拌完成时,开关阀B4.8打开,混有氧化剂的陶瓷污泥颗粒从出料口B4.7进入干燥装置5。所述搅拌混合装置4主要用于加入氧化剂和将氧化剂与陶瓷污泥颗粒充分混合,便于后续对絮凝剂进行断链处理。Specifically, as shown in FIG. 4 , the stirring and mixing
具体的,如图5所示,所述干燥装置5包括密封的输送通道5.1、若干超声波发生机构和若干微波发生器5.3。所述输送通道5.1的底部设有输送带B5.4,输送通道5.1的一端为输入端,另一端为输出端(图中箭头所指方向为输送带运动方向,以输送带的运动方向为后方),所述输入端的上方设有进料口C5.5,进料口C5.5的正上方为搅拌混合装置的出料口B4.7,从出料口B4.7落出的陶瓷污泥颗粒刚好落在输送带B5.4,并且随输送带B5.4的运动,逐渐往后方运动;输送通道5.1的输入端还设有热风出口5.7,所述热风出口5.7通过排气管将气体排出,输送通道5.1的输出端设有热风入口5.6,所述热风入口5.6通过管道连通陶瓷窑炉的排风口,利用陶瓷生产线中窑炉通风的余热对陶瓷污泥进行干燥,所述热风入口5.6和热风出口5.7均设有金属网5.9,用于防止输送通道内微波外泄;所述超声波发生机构包括超声波换能器5.8和超声波发生器5.2,所述超声波换能器设置于输送通道5.1的内侧壁上,超声波发生器5.2设置于输送通道5.1的外部,所述超声波换能器5.8与超声波发生器5.2电性连接;所述微波发生器5.3也设置于的内侧壁上,并且超声波换能器5.8与微波发生器5.3间隔设置。Specifically, as shown in FIG. 5 , the drying device 5 includes a sealed conveying channel 5.1, several ultrasonic generating mechanisms and several microwave generators 5.3. The bottom of the conveying channel 5.1 is provided with a conveying belt B5.4, one end of the conveying channel 5.1 is the input end, and the other end is the output end (the direction indicated by the arrow in the figure is the moving direction of the conveying belt, and the moving direction of the conveying belt is the rear. ), there is a feeding port C5.5 above the input end, and the discharge port B4.7 of the stirring and mixing device is directly above the feeding port C5.5, and the ceramic sludge falling from the discharging port B4.7 The particles just fall on the conveyor belt B5.4, and gradually move backward with the movement of the conveyor belt B5.4; the input end of the conveying channel 5.1 is also provided with a hot air outlet 5.7, and the hot air outlet 5.7 discharges the gas through the exhaust pipe , the output end of the conveying channel 5.1 is provided with a hot air inlet 5.6, the hot air inlet 5.6 is connected to the exhaust port of the ceramic kiln through a pipeline, and the waste heat of the kiln ventilation in the ceramic production line is used to dry the ceramic sludge. The hot air inlet 5.6 Both the hot air outlet 5.7 and the hot air outlet 5.7 are provided with a metal mesh 5.9 to prevent the leakage of microwaves in the conveying channel; the ultrasonic generating mechanism includes an ultrasonic transducer 5.8 and an ultrasonic generator 5.2, and the ultrasonic On the inner side wall, the ultrasonic generator 5.2 is arranged on the outside of the conveying channel 5.1, and the ultrasonic transducer 5.8 is electrically connected with the ultrasonic generator 5.2; the microwave generator 5.3 is also arranged on the inner side wall, and the ultrasonic transducer The generator 5.8 is spaced apart from the microwave generator 5.3.
作为一种优选的实施方式,如图7所示,所述超声波换能器均布于输送通道前2/3段的侧壁上,所述微波发生器均布于输送通道后2/3段的侧壁段上。这是因为,陶瓷污泥的干燥过程是随着输送带的前进,其含水率是逐渐下降的,在输送通道的前段,含水率较高,而超声波对含水率高的介质处理效果较明显,但是污泥中过多水分会消耗微波能量,降低微波的作用效果。因此,将超声波换能器设置于输送通道的前2/3段的侧壁上,使干燥的前期,主要通过超声波对陶瓷污泥起作用,超声波与氧化剂结合促使絮凝剂降解。将微波发生器设置于输送通道后2/3段的侧壁上,处理外表已经比较干燥污泥,使微波由内而外的热效应更好的发挥作用,从而在保证处理效果的前提下使整体的能耗降低。As a preferred embodiment, as shown in FIG. 7 , the ultrasonic transducers are evenly distributed on the sidewall of the first 2/3 section of the conveying channel, and the microwave generators are evenly distributed on the rear 2/3 section of the conveying channel on the side wall section. This is because the drying process of ceramic sludge is that with the advancement of the conveyor belt, the moisture content of the sludge gradually decreases. However, too much water in the sludge will consume microwave energy and reduce the effect of microwave. Therefore, the ultrasonic transducer is arranged on the side wall of the first 2/3 section of the conveying channel, so that in the early stage of drying, ultrasonic waves are mainly used to act on the ceramic sludge, and the combination of ultrasonic waves and oxidants promotes the degradation of the flocculant. The microwave generator is arranged on the side wall of the rear 2/3 section of the conveying channel to treat the sludge that has been relatively dry on the outside, so that the thermal effect of the microwave from the inside to the outside can play a better role, so as to ensure the overall treatment effect. energy consumption is reduced.
优选的,如图6所示,所述输送通道的外壳6为金属外壳,输送通道的内壁设有微波屏蔽层7和隔音层8,所述微波屏蔽层7为金属层,在微波屏蔽层和外壳之间填充有耐热吸音材料,形成隔音层8。设置的微波屏蔽层主要作用是使微波能通过金属的反射,更好的对陶瓷污泥产生热解效应,同时防止微波外泄,对人体造成辐射,设置的隔音层主要作用是防止超声波传递至外,形成较大的噪声。Preferably, as shown in FIG. 6 , the outer shell 6 of the transport channel is a metal shell, and the inner wall of the transport channel is provided with a microwave shielding layer 7 and a
上述结构的干燥装置工作时,热风从输送通道的输出端吹入,起到将陶瓷污泥中的水分蒸发带走的作用,同时,超声波换能器产生的超声波,能促进陶瓷污泥中絮凝剂降解,提高污泥干燥的效率和易分散性。而微波发生器产生的微波,由内而外的对陶瓷污泥加热,促进陶瓷污泥分散,加速陶瓷污泥中水分的蒸发。When the drying device of the above structure works, the hot air is blown in from the output end of the conveying channel, which plays the role of evaporating away the water in the ceramic sludge. At the same time, the ultrasonic wave generated by the ultrasonic transducer can promote the flocculation in the ceramic sludge. agent degradation, improve the efficiency and ease of dispersibility of sludge drying. The microwave generated by the microwave generator heats the ceramic sludge from the inside out, which promotes the dispersion of the ceramic sludge and accelerates the evaporation of water in the ceramic sludge.
进一步的,上述结构的干燥装置中,由于热风流动方向和污泥输送方向相反,可以使后端较干燥的污泥与传输装置后端热风入口处较干燥的热风充分接触,提高污泥干燥效率,降低最终陶瓷微粉含水率。而微波可以快速穿透陶瓷污泥,由内而外的加热污泥内部水分,使得陶瓷颗粒间的间隙水和结合水向外溢出,随后被热风带走。Further, in the drying device of the above structure, since the hot air flow direction is opposite to the sludge conveying direction, the drier sludge at the rear end can be fully contacted with the drier hot air at the hot air inlet at the rear end of the transmission device, thereby improving the sludge drying efficiency. , reduce the moisture content of the final ceramic powder. The microwave can quickly penetrate the ceramic sludge and heat the internal water of the sludge from the inside out, so that the interstitial water and the bound water between the ceramic particles overflow to the outside, and are then taken away by the hot air.
更进一步的,上述结构的干燥装置能使高分子链的絮凝剂在超声波、氧化剂以及热辐射的三重作用下,快速降解断裂成短链分子,从而使絮凝团聚的陶瓷污泥分散成陶瓷污泥颗粒。并且,断裂后的带同种电荷的絮凝剂短链分子,通过吸附在陶瓷颗粒上使陶瓷颗粒带上同种电荷,降低陶瓷颗粒与水分子间的作用力,促使陶瓷污泥颗粒间的间隙水和结合水分更易蒸发。同时,带同种电荷的陶瓷颗粒通过静电斥力、微波由内而外的热效应,实现了陶瓷污泥团的崩解与陶瓷颗粒的相对分散。在超声波、氧化剂、高频微波辐射和热风干燥的多重作用下,可使含水率较高的陶瓷污泥快速干燥,得到分散的陶瓷微粉颗粒。Further, the drying device of the above structure can make the flocculant of the polymer chain rapidly degrade and break into short-chain molecules under the triple action of ultrasonic waves, oxidants and heat radiation, so that the flocculated and aggregated ceramic sludge can be dispersed into ceramic sludge. particles. In addition, the short-chain flocculant molecules with the same charge after the fracture are adsorbed on the ceramic particles, so that the ceramic particles are charged with the same charge, which reduces the force between the ceramic particles and the water molecules, and promotes the gap between the ceramic sludge particles. Water and bound moisture evaporate more easily. At the same time, the ceramic particles with the same charge realize the disintegration of the ceramic sludge mass and the relative dispersion of the ceramic particles through the electrostatic repulsion and the thermal effect of the microwave from the inside to the outside. Under the multiple actions of ultrasonic wave, oxidant, high-frequency microwave radiation and hot air drying, the ceramic sludge with high water content can be quickly dried to obtain dispersed ceramic micropowder particles.
上述结构的陶瓷污泥处理系统,还设有控制机构,所述控制机构分别与絮凝装置1、脱水装置2、粉碎过筛装置3、搅拌混合装置4、干燥装置5电性连接,用于控制絮凝装置、脱水装置、粉碎过筛装置、搅拌混合装置、干燥装置的开启和关闭,同时控制絮凝剂的添加、氧化剂的添加,以及控制各搅拌器的转速、超声波发生器的频率、微波发生器的频率。设置的控制机构,能实现对陶瓷污泥处理系统全自动化控制,极大的提高了生产效率及生产的安全性。The ceramic sludge treatment system of the above structure is also provided with a control mechanism, which is electrically connected to the
本实用新型提供了一种陶瓷污泥处理系统,所述系统通过设置絮凝装置、脱水装置、粉碎过筛装置、搅拌混合装置、干燥装置,实现了絮凝-初步脱水-粉碎过筛-加氧化剂-深度脱水和絮凝剂的破坏的陶瓷污泥处理工艺,处理后的陶瓷污泥变成分散的颗粒,含水率低,利用价值高。The utility model provides a ceramic sludge treatment system, which realizes flocculation-preliminary dehydration-crushing and sieving-adding oxidant- The ceramic sludge treatment process of deep dewatering and flocculant destruction, the treated ceramic sludge becomes dispersed particles with low moisture content and high utilization value.
可以理解的是,对本领域普通技术人员来说,可以根据本实用新型的技术方案及其构思加以等同替换或改变,而所有这些改变或替换都应属于本实用新型所附的权利要求的保护范围。It can be understood that, for those of ordinary skill in the art, equivalent replacements or changes can be made according to the technical solutions of the present invention and the concept thereof, and all these changes or replacements should belong to the protection scope of the appended claims of the present invention. .
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WO2022021808A1 (en) * | 2020-07-29 | 2022-02-03 | 水木金谷环境科技有限公司 | Ceramic sludge treatment system |
WO2022022270A1 (en) * | 2020-07-29 | 2022-02-03 | 水木金谷环境科技有限公司 | Ceramic sludge treatment method and system |
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