CN112404110B - Method and system for treating waste salt containing organic matter using double-cycle thermal purification technology - Google Patents
Method and system for treating waste salt containing organic matter using double-cycle thermal purification technology Download PDFInfo
- Publication number
- CN112404110B CN112404110B CN202011377335.7A CN202011377335A CN112404110B CN 112404110 B CN112404110 B CN 112404110B CN 202011377335 A CN202011377335 A CN 202011377335A CN 112404110 B CN112404110 B CN 112404110B
- Authority
- CN
- China
- Prior art keywords
- waste salt
- flue gas
- thermal
- kiln
- thermal kiln
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Active
Links
- 150000003839 salts Chemical class 0.000 title claims abstract description 145
- 239000002699 waste material Substances 0.000 title claims abstract description 53
- 238000000746 purification Methods 0.000 title claims abstract description 48
- 238000000034 method Methods 0.000 title claims abstract description 28
- 238000005516 engineering process Methods 0.000 title claims abstract description 23
- 239000005416 organic matter Substances 0.000 title claims description 32
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 101
- 239000003546 flue gas Substances 0.000 claims abstract description 101
- 239000002440 industrial waste Substances 0.000 claims abstract description 42
- 239000010815 organic waste Substances 0.000 claims abstract description 34
- 238000002485 combustion reaction Methods 0.000 claims abstract description 24
- 239000000428 dust Substances 0.000 claims abstract description 22
- 230000008569 process Effects 0.000 claims abstract description 5
- 238000010438 heat treatment Methods 0.000 claims description 7
- 238000006243 chemical reaction Methods 0.000 claims description 6
- 239000007789 gas Substances 0.000 claims description 4
- 239000000779 smoke Substances 0.000 claims 1
- 238000000926 separation method Methods 0.000 abstract description 9
- 239000012535 impurity Substances 0.000 abstract description 8
- 230000008018 melting Effects 0.000 abstract description 6
- 238000002844 melting Methods 0.000 abstract description 6
- 238000004064 recycling Methods 0.000 abstract description 4
- 238000009270 solid waste treatment Methods 0.000 abstract description 2
- 238000010992 reflux Methods 0.000 abstract 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 12
- 238000005054 agglomeration Methods 0.000 description 6
- 230000002776 aggregation Effects 0.000 description 6
- 229910052757 nitrogen Inorganic materials 0.000 description 6
- 239000002894 chemical waste Substances 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 5
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 238000004043 dyeing Methods 0.000 description 2
- 230000036541 health Effects 0.000 description 2
- 239000003345 natural gas Substances 0.000 description 2
- 239000000575 pesticide Substances 0.000 description 2
- 238000010791 quenching Methods 0.000 description 2
- 230000000171 quenching effect Effects 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000009692 water atomization Methods 0.000 description 2
- 238000013459 approach Methods 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 230000009977 dual effect Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000012847 fine chemical Substances 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 239000002920 hazardous waste Substances 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- -1 pharmaceutical Substances 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 238000000197 pyrolysis Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 239000002352 surface water Substances 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 238000004056 waste incineration Methods 0.000 description 1
Images
Classifications
-
- 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
- B09B3/40—Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B5/00—Operations not covered by a single other subclass or by a single other group in this subclass
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/06—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F27—FURNACES; KILNS; OVENS; RETORTS
- F27D—DETAILS OR ACCESSORIES OF FURNACES, KILNS, OVENS OR RETORTS, IN SO FAR AS THEY ARE OF KINDS OCCURRING IN MORE THAN ONE KIND OF FURNACE
- F27D17/00—Arrangements for using waste heat; Arrangements for using, or disposing of, waste gases
- F27D17/10—Arrangements for using waste heat
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F27—FURNACES; KILNS; OVENS; RETORTS
- F27D—DETAILS OR ACCESSORIES OF FURNACES, KILNS, OVENS OR RETORTS, IN SO FAR AS THEY ARE OF KINDS OCCURRING IN MORE THAN ONE KIND OF FURNACE
- F27D17/00—Arrangements for using waste heat; Arrangements for using, or disposing of, waste gases
- F27D17/20—Arrangements for treatment or cleaning of waste gases
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
技术领域technical field
本发明涉及固体废弃物处理技术领域,尤其是涉及一种采用双循环热力净化技术处理含有机物废盐的方法及系统。The invention relates to the technical field of solid waste treatment, in particular to a method and system for treating waste salt containing organic matter by adopting double-cycle thermal purification technology.
背景技术Background technique
废盐的产生企业主要包括煤化工、农药、制药、精细化工、印染等国家重点工业。化工废盐污染非常严重,直接危害人体健康,破坏生态环境,可以造成地表水、地下水水质恶化,土地的盐碱化等。Waste salt producers mainly include coal chemical industry, pesticide, pharmaceutical, fine chemical industry, printing and dyeing and other national key industries. Chemical waste salt pollution is very serious, directly endangering human health, destroying the ecological environment, and can cause deterioration of surface water and groundwater quality, and salinization of land.
废盐数量巨大,再生产品市场有限,原盐价值低,提纯成本高,有可能进入食物链,直接危害人体健康,其无害化管理难度很大。目前废盐的无害化管理措施主要包括:减排、生产化工原料、排海和填埋。The amount of waste salt is huge, the market for recycled products is limited, the value of raw salt is low, and the cost of purification is high. It may enter the food chain and directly endanger human health. Its harmless management is very difficult. At present, the harmless management measures of waste salt mainly include: emission reduction, production of chemical raw materials, sea discharge and landfill.
随着环保要求的提高,现有处置手段,已经不能满足废盐无害化管理的要求,特别是对于农药、医药和印染三大行业,废盐的处置已经成为制约行业发展的瓶颈。With the improvement of environmental protection requirements, the existing disposal methods can no longer meet the requirements of harmless management of waste salt, especially for the three major industries of pesticides, medicine and printing and dyeing, the disposal of waste salt has become a bottleneck restricting the development of the industry.
由于废盐产生量大、不宜焚烧、限制填埋等特点,废盐的资源化处置是一条可行的无害化管理途径,然而,目前国内外并没有成熟的化工废盐资源化处置技术,废盐的资源处置涉及到有机物去除、杂质去除和分盐等各种关键技术,均有待进一步突破。Due to the large amount of waste salt produced, unsuitable for incineration, and restricted landfill, the resource disposal of waste salt is a feasible and harmless management approach. However, there is no mature resource disposal technology for chemical waste salt at home and abroad. The disposal of salt resources involves various key technologies such as organic matter removal, impurity removal and salt separation, all of which need further breakthroughs.
其中,有机物去除作为废盐资源化利用中的关键环节,如何能够把废盐中的TOC(总有机碳)降低至100ppm以下,为后续的除杂和分盐工艺打下良好的基础,同时如何能够通过多能源渠道、废盐和烟气双循环技术的应用,实现最佳的能源实践,避免废盐处理中熔融结块现象的发生,成为本领域技术人员亟待解决的技术问题。Among them, the removal of organic matter is a key link in the resource utilization of waste salt. How can the TOC (total organic carbon) in waste salt be reduced to below 100ppm to lay a good foundation for subsequent impurity removal and salt separation processes? Through the application of multi-energy channels, waste salt and flue gas dual cycle technology, to achieve the best energy practice and avoid the occurrence of melting and agglomeration in waste salt treatment has become a technical problem to be solved urgently by those skilled in the art.
发明内容Contents of the invention
有鉴于此,本发明的目的之一在于提供一种采用双循环热力净化技术处理含有机物废盐的方法,以解决现有技术中干化后的化工废盐,其TOC(总有机碳)含量从800ppm至20000ppm不等,从而不能为后续的除杂和分盐工艺打下良好的基础,以及废盐处理中出现熔融结块的技术问题。In view of this, one of the purposes of the present invention is to provide a method for treating waste salt containing organic matter using dual-cycle thermal purification technology to solve the problem of TOC (total organic carbon) content of the dried chemical waste salt in the prior art. It varies from 800ppm to 20000ppm, so it cannot lay a good foundation for the subsequent impurity removal and salt separation process, and there is a technical problem of melting and agglomeration in waste salt treatment.
本发明的目的之二在于提供一种采用双循环热力净化技术处理含有机物废盐的系统。The second object of the present invention is to provide a system for treating waste salt containing organic matter using double-cycle thermal purification technology.
为了实现上述目的之一,本发明提供了一种采用双循环热力净化技术处理含有机物废盐的方法,所述方法包括:In order to achieve one of the above objectives, the present invention provides a method for treating waste salt containing organic matter by adopting double-cycle thermal purification technology, the method comprising:
有机物废盐经进料仓进入热力窑后分解为净化工业废盐和烟气;Organic waste salt is decomposed into purified industrial waste salt and flue gas after entering the thermal kiln through the feed bin;
所述净化工业废盐进入中间仓后分为两路,一路通过变频的回流输送系统再循环进入所述进料仓,与所述进料仓中未经过处理的所述有机物废盐混合,一起再进入所述热力窑,一路通过成品仓向外排放;The purified industrial waste salt is divided into two paths after entering the intermediate bin, and one path is recirculated into the feed bin through the frequency conversion return conveying system, and mixed with the untreated organic waste salt in the feed bin, together Enter the thermal kiln again, and discharge outwards through the finished product warehouse all the way;
所述烟气经过除尘、燃烧和净化后分为两路,一路循环至所述热力窑,一路向外排放。The flue gas is divided into two paths after dust removal, combustion and purification, one path is circulated to the thermal kiln, and the other path is discharged outward.
根据一种优选实施方式,所述有机物废盐进入所述进料仓之前需要经过预处理,然后经所述进料仓进入所述热力窑,在所述热力窑中停留30-120min,所述有机物废盐中的有机物被热分解为所述烟气和所述净化工业废盐。According to a preferred embodiment, the organic waste salt needs to be pretreated before entering the feed bin, and then enters the thermal kiln through the feed bin, and stays in the thermal kiln for 30-120min. The organic matter in the organic matter waste salt is thermally decomposed into the flue gas and the purified industrial waste salt.
根据一种优选实施方式,所述热力窑采用回转式热力窑,倾斜角度为2°-5°,热力窑360度自转。According to a preferred embodiment, the thermal kiln is a rotary thermal kiln with an inclination angle of 2°-5°, and the thermal kiln rotates 360 degrees.
根据一种优选实施方式,所述热力窑通过转动电机驱动转动,改变所述转动电机的频率,调整所述有机物废盐在所述热力窑中的停留时间。According to a preferred embodiment, the thermal kiln is driven to rotate by a rotating motor, and the frequency of the rotating motor is changed to adjust the residence time of the organic waste salt in the thermal kiln.
根据一种优选实施方式,所述热力窑的温度在300℃-600℃范围内可调,温度的调整可以通过改变所述热力窑的加热装置的功率、所述烟气的燃烧温度以及循环烟气的流量。According to a preferred embodiment, the temperature of the thermal kiln is adjustable within the range of 300°C-600°C, and the temperature can be adjusted by changing the power of the heating device of the thermal kiln, the combustion temperature of the flue gas and the circulating flue gas gas flow.
根据一种优选实施方式,所述加热装置为电加热器或者燃烧器。According to a preferred embodiment, the heating device is an electric heater or a burner.
根据一种优选实施方式,所述循环烟气切向进入所述热力窑的窑尾。According to a preferred embodiment, the circulating flue gas enters the kiln tail of the thermal kiln tangentially.
根据一种优选实施方式,所述热力窑的窑头罩采用沉降式结构分离所述净化工业废盐和所述烟气。According to a preferred embodiment, the kiln hood of the thermal kiln adopts a sinking structure to separate the purified industrial waste salt and the flue gas.
为了实现上述目的之二,本发明提供了一种采用双循环热力净化技术处理含有机物废盐的系统,包括有机物废盐处理系统和烟气处理系统,其中:In order to achieve the above-mentioned second objective, the present invention provides a system for treating waste salt containing organic matter by adopting double-cycle thermal purification technology, including a waste organic salt treatment system and a flue gas treatment system, wherein:
所述有机物废盐处理系统包括进料仓、用于分解有机物废盐的热力窑、中间仓和成品仓以及回流输送系统,所述进料仓、所述热力窑、所述中间仓以及所述成品仓顺次首尾相接并连通,所述热力窑分解所述有机物废盐形成净化工业废盐和烟气,所述热力窑同时通过所述回流输送系统与所述进料仓连接并连通,所述净化工业废盐一路通过所述回流输送系统回流至所述进料仓,一路通过所述成品仓向外排放;The organic waste salt treatment system includes a feed bin, a thermal kiln for decomposing organic waste salt, an intermediate bin, a finished product bin, and a return conveying system. The feed bin, the thermal kiln, the intermediate bin, and the The finished product bins are connected end to end and communicated in sequence. The thermal kiln decomposes the organic waste salt to form purified industrial waste salt and flue gas. The thermal kiln is connected and communicated with the feed bin through the return conveying system at the same time. The purified industrial waste salt flows back to the feed bin through the return conveying system all the way, and discharges outward through the finished product bin all the way;
所述烟气处理系统与所述热力窑连接并连通,所述烟气从所述热力窑排出后经过所述烟气处理系统处理,一路循环至所述热力窑,一路向外排放。The flue gas treatment system is connected and communicated with the thermal kiln, and after being discharged from the thermal kiln, the flue gas is processed by the flue gas treatment system, circulated all the way to the thermal kiln, and is discharged all the way to the outside.
根据一种优选实施方式,所述烟气处理系统包括除尘器、燃烧室、烟气净化装置以及循环风机,所述除尘器与所述热力窑连接并连通,所述除尘器、所述燃烧室、所述烟气净化装置以及所述循环风机顺次首尾相接,所述烟气从所述热力窑排出先后经过所述除尘器除尘,所述燃烧室燃烧以及所述烟气净化装置净化后,通过循环风机循环至所述热力窑。According to a preferred embodiment, the flue gas treatment system includes a dust collector, a combustion chamber, a flue gas purification device and a circulating fan, the dust collector is connected and communicated with the thermal kiln, the dust collector, the combustion chamber , the flue gas purification device and the circulating fan are connected end to end in sequence, the flue gas is discharged from the thermal kiln and passes through the dust collector successively for dust removal, after the combustion chamber is burned and the flue gas purification device purifies , circulated to the thermal kiln through a circulating fan.
根据一种优选实施方式,还包括引风机和烟囱,所述引风机同时与所述烟囱和所述烟气净化装置连接,所述引风机用于向外排放经过所述烟气净化装置净化后的达标烟气。According to a preferred embodiment, it also includes an induced draft fan and a chimney, the induced draft fan is connected to the chimney and the flue gas purification device at the same time, and the induced draft fan is used to discharge the gas after being purified by the flue gas purification device to the outside standard flue gas.
根据一种优选实施方式,所述烟气净化装置包括半干法急冷脱酸塔、SNCR、布袋除尘器、烟气冷凝器和烟气换热器。According to a preferred embodiment, the flue gas purification device includes a semi-dry quenching deacidification tower, an SNCR, a bag filter, a flue gas condenser and a flue gas heat exchanger.
根据一种优选实施方式,所述热力窑设置为回转式窑炉,倾斜角度为2°-5°。According to a preferred embodiment, the thermal kiln is set as a rotary kiln with an inclination angle of 2°-5°.
根据一种优选实施方式,所述热力窑底部安装转动电机,所述转动电机与所述热力窑驱动连接,所述转动电机的频率可变。According to a preferred embodiment, a rotating motor is installed at the bottom of the thermal kiln, the rotating motor is drivingly connected to the thermal kiln, and the frequency of the rotating motor is variable.
根据一种优选实施方式,所述热力窑上安装电加热器,所述电加热器分为三个独立回路,用于控制所述热力窑的温度。According to a preferred embodiment, an electric heater is installed on the thermal kiln, and the electric heater is divided into three independent circuits for controlling the temperature of the thermal kiln.
根据一种优选实施方式,所述热力窑上安装燃烧器,通过控制所述燃烧器的功率调整所述热力窑温度。According to a preferred embodiment, a burner is installed on the thermal kiln, and the temperature of the thermal kiln is adjusted by controlling the power of the burner.
根据一种优选实施方式,所述热力窑的窑头处设置加湿水雾化喷枪和水流量控制回路,用于控制所述热力窑的水量。According to a preferred embodiment, the kiln head of the thermal kiln is provided with a humidifying water atomization spray gun and a water flow control circuit for controlling the water volume of the thermal kiln.
根据一种优选实施方式,所述热力窑的窑头处设置氮气喷头和氮气流量控制回路,用于控制所述热力窑的氮气量。According to a preferred embodiment, the kiln head of the thermal kiln is provided with a nitrogen nozzle and a nitrogen flow control circuit for controlling the nitrogen volume of the thermal kiln.
根据一种优选实施方式,所述热力窑的窑头罩设置为沉降式结构。According to a preferred embodiment, the kiln hood of the thermal kiln is set as a submerged structure.
本发明提供的采用双循环热力净化技术处理含有机物废盐的方法,具有以下技术效果:The method provided by the present invention for treating waste salt containing organic matter by adopting double-cycle thermal purification technology has the following technical effects:
该种方法主要由两个循环热力净化技术组成,其一为净化工业废盐进入中间仓后,通过变频的回流输送系统在循环进入进料仓,与进料仓中未经过处理的有机物废盐混合,一起再进入热力窑,其二为烟气经过除尘、燃烧和净化后分为两路,一路再循环至热力窑,一路烟气达标后向外排放,采用该种双循环的方式能够将干化后的有机物废盐的TOC含量从800ppm至20000ppm降到100ppm以下,以满足进一步除杂和分盐需要,实现废盐资源化利用,同时净化工业废盐再循环,还能够克服有机物废盐处理过程中出现的熔融结块现象。This method is mainly composed of two cycle thermal purification technologies. One is to purify industrial waste salt after entering the intermediate bin, and then enter the feeding bin through the frequency conversion backflow conveying system, and the untreated organic waste salt in the feeding bin The second is that the flue gas is divided into two paths after dust removal, combustion and purification, one path is recirculated to the thermal kiln, and the flue gas in the other path is discharged outside after reaching the standard. This double circulation method can The TOC content of the dried organic waste salt is reduced from 800ppm to 20000ppm to less than 100ppm to meet the needs of further impurity removal and salt separation, realize the resource utilization of waste salt, purify industrial waste salt and recycle, and overcome the problem of organic waste salt Melting agglomeration that occurs during processing.
本发明提供的采用双循环热力净化技术处理含有机物废盐的系统,具有以下技术效果:The system provided by the present invention adopts double-cycle thermal purification technology to treat waste salt containing organic matter, and has the following technical effects:
该种系统与上述的方法对应,即主要由有机物废盐处理系统和烟气处理系统组成,有机物处理系统则包括进料仓、用于分解有机物废盐的热力窑、中间仓和成品仓以及回流输送系统,进料仓、热力窑、中间仓以及成品仓顺次首尾相接并连通,热力窑分解有机物废盐形成净化工业废盐和烟气,热力窑同时通过回流输送系统与进料仓连接并连通,形成一路循环,净化工业废盐通过回流输送系统回流至进料仓;而另一路的循环为烟气循环,烟气处理系统与热力窑连接并连通,烟气从热力窑排出后经过烟气处理系统处理,回流至循环至热力窑。采用该种双循环系统能够将干化后的有机物废盐的TOC含量从800ppm至20000ppm降到100ppm以下,以满足进一步除杂和分盐需要,实现废盐资源化利用,同时净化工业废盐再循环,还能够克服有机物废盐处理过程中出现的熔融结块现象。This system corresponds to the above-mentioned method, that is, it is mainly composed of an organic matter waste salt treatment system and a flue gas treatment system. The organic matter treatment system includes a feed bin, a thermal kiln for decomposing organic matter waste salt, an intermediate bin, a finished product bin, and a return flow Conveyor system, feeding bin, thermal kiln, intermediate bin and finished product bin are connected end-to-end and connected in sequence. The thermal kiln decomposes organic waste salt to form purified industrial waste salt and flue gas. The thermal kiln is connected to the feeding bin through the return conveying system at the same time. And connected to form a cycle, the purified industrial waste salt is returned to the feed bin through the return conveying system; while the other cycle is the flue gas cycle, the flue gas treatment system is connected and communicated with the thermal kiln, and the flue gas is discharged from the thermal kiln and passes through The flue gas treatment system treats and returns to the thermal kiln for circulation. The use of this double circulation system can reduce the TOC content of the dried organic waste salt from 800ppm to 20000ppm to below 100ppm, so as to meet the needs of further impurity removal and salt separation, realize the resource utilization of waste salt, and purify industrial waste salt at the same time. It can also overcome the melting and agglomeration phenomenon in the process of organic waste salt treatment.
附图说明Description of drawings
为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施例或现有技术描述中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本发明的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据这些附图获得其他的附图。In order to more clearly illustrate the technical solutions in the embodiments of the present invention or the prior art, the following will briefly introduce the drawings that need to be used in the description of the embodiments or the prior art. Obviously, the accompanying drawings in the following description are only These are some embodiments of the present invention. Those skilled in the art can also obtain other drawings based on these drawings without creative work.
图1是本发明一实施例的采用双循环热力净化技术处理含有机物废盐的系统的流程图;Fig. 1 is a flow chart of a system for treating waste salt containing organic matter using dual-cycle thermal purification technology according to an embodiment of the present invention;
图2是图1中热力窑的结构示意图;Fig. 2 is the structural representation of thermal kiln among Fig. 1;
图3是图2中热力窑的窑尾沿A-A方向的剖视图;Fig. 3 is the sectional view of the kiln tail of thermal kiln in Fig. 2 along A-A direction;
其中,图1-图3:Among them, Figure 1-Figure 3:
1、有机物废盐处理系统;101、进料仓;102、热力窑;1021、沉降式结构;1022、转动电机;1023、电加热器;1024、窑尾;103、中间仓;104、成品仓;1. Organic matter waste salt treatment system; 101, feed bin; 102, thermal kiln; 1021, sinking structure; 1022, rotating motor; 1023, electric heater; 1024, kiln tail; 103, intermediate bin; 104, finished product bin ;
2、烟气处理系统;201、除尘器;202、燃烧室;203、烟气净化装置;204、循环风机;205、引风机;206、烟囱。2. Flue gas treatment system; 201, dust collector; 202, combustion chamber; 203, flue gas purification device; 204, circulating fan; 205, induced draft fan; 206, chimney.
具体实施方式Detailed ways
为使本发明的目的、技术方案和优点更加清楚,下面将对本发明的技术方案进行详细的描述。显然,所描述的实施例仅仅是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动的前提下所得到的所有其它实施方式,都属于本发明所保护的范围。In order to make the purpose, technical solution and advantages of the present invention clearer, the technical solution of the present invention will be described in detail below. Apparently, the described embodiments are only some of the embodiments of the present invention, but not all of them. Based on the embodiments of the present invention, all other implementations obtained by persons of ordinary skill in the art without making creative efforts fall within the protection scope of the present invention.
下面结合实施例对本发明的技术方案进行进一步的阐述。The technical solutions of the present invention will be further described below in conjunction with the embodiments.
本发明一实施例提供的采用双循环热力净化技术处理含有机物废盐的方法,该方法包括:有机物废盐经进料仓101进入热力窑102后分解为净化工业废盐和烟气;净化工业废盐进入中间仓103后分为两路,一路通过变频的回流输送系统再循环进入进料仓101,与进料仓101中未经过处理的有机物废盐混合,一起再进入热力窑102,一路通过成品仓104向外排放;烟气经过除尘、燃烧和净化后分为两路,一路循环至热力窑102,一路向外排放。An embodiment of the present invention provides a method for treating waste salt containing organic matter using a double-cycle thermal purification technology. The method includes: waste organic salt enters a
上述方法可用于化工废盐的无害化资源化处理,干化后的化工废盐,其TOC含量从800ppm到20000ppm不等,经双循环热力净化系统处理后,即有机物废盐在热力窑102分解为净化工业废盐和烟气,净化工业废盐进入中间仓103后再通过变频的回流输送系统循环进入进料仓101,达到循环处理的目的,而烟气则经过除尘、燃烧和净化后也循环至热力窑102,从而使废盐中TOC含量降低至100ppm以下,满足进一步除杂和分盐,实现废盐资源化的要求。The above method can be used for the harmless and resourceful treatment of chemical waste salt. The TOC content of the dried chemical waste salt ranges from 800ppm to 20000ppm. It is decomposed into purified industrial waste salt and flue gas. The purified industrial waste salt enters the
进一步的,有机物废盐进入进料仓101之前需要经过预处理,然后经进料仓101进入热力窑102,在热力窑102中停留30-120min,有机物废盐中的有机物被热分解为烟气和净化工业废盐,而净化工业废盐经过热力窑102的窑尾1024排出至中间仓103,烟气则经过除尘、燃烧和净化处理。Further, the organic waste salt needs to be pretreated before entering the
进一步的,热力窑102采用回转式热力窑102,倾斜角度为2°-5°,热力窑102 360度自转,具体是与转动电机1022驱动连接,通过转动电机1022驱动转动,改变转动电机1022的频率,可调整有机物废盐在热力窑102中的停留时间,即在热力窑102中停留时间的范围为30-120min。Further, the
进一步的,热力窑102的温度在300℃-600℃范围内可调,温度的调整可以通过改变热力窑102的加热装置功率、烟气的燃烧温度以及循环烟气的流量。Further, the temperature of the
需要说明的是,本发明的加热装置可以为电加热器1023、可以为燃烧器,还可以为其他类型的加热装置,只要能够实现对热力窑的加热功能,均在本发明的保护范围之内,本发明对此不作限定。It should be noted that the heating device of the present invention can be an
进一步的,循环烟气切向进入热力窑102的窑尾1024,即具体是循环烟气从热力窑102的窑尾1024 270°切向进入,如图2-3所示,烟气在热力窑102中旋转向前,从而增大了与热力窑102底部的有机物废盐的接触面积,达到充分接触的效果。Further, the circulating flue gas enters the
进一步的,热力窑102的窑头罩采用沉降式结构1021,分离净化工业废盐和烟气,从而实现净化工业废盐和烟气的分离,减少被烟气携带进入燃烧室202的净化工业废盐的数量。Furthermore, the kiln hood of the
本发明另一实施例提供了一种采用双循环热力净化技术处理含有机物废盐的系统,如图1-图3所示,包括有机物废盐处理系统1和烟气处理系统2,有机物处理系统包括进料仓101、用于分解有机物废盐的热力窑102、中间仓103和成品仓104以及回流输送系统,进料仓101、热力窑102、中间仓103以及成品仓104顺次首尾相接并连通,热力窑102分解有机物废盐形成净化工业废盐和烟气,热力窑102同时通过回流输送系统与进料仓101连接并连通,净化工业废盐一路通过回流输送系统回流至进料仓101,一路通过成品仓104向外排放;烟气处理系统2与热力窑102连接并连通,烟气从热力窑102排出后经过烟气处理系统2处理,一路循环至热力窑102,一路向外排放。Another embodiment of the present invention provides a system for treating waste salt containing organic matter using double-cycle thermal purification technology, as shown in Figures 1-3, including a waste organic salt treatment system 1 and a flue gas treatment system 2, the organic matter treatment system
本实施例的系统与上述实施例的方法对应,即主要由有机物废盐处理系统1和烟气处理系统2组成,有机物废盐处理系统1则包括进料仓101、用于分解有机物废盐的热力窑102、中间仓103和成品仓104以及回流输送系统,进料仓101、热力窑102、中间仓103以及成品仓104顺次首尾相接并连通,热力窑102分解有机物废盐形成净化工业废盐和烟气,热力窑102同时通过回流输送系统与进料仓101连接并连通,形成一路循环,净化工业废盐通过回流输送系统回流至进料仓101;而另一路的循环为烟气循环,烟气处理系统2与热力窑102连接并连通,烟气从热力窑102排出后经过烟气处理系统2处理,回流至循环至热力窑102。采用该种双循环系统能够将干化后的有机物废盐的TOC含量从800ppm至20000ppm降到100ppm以下,以满足进一步除杂和分盐需要,实现废盐资源化利用,同时净化工业废盐在循环,还能够克服有机物废盐处理过程中出现的熔融结块现象。The system of this embodiment corresponds to the method of the above-mentioned embodiment, that is, it is mainly composed of a waste organic salt treatment system 1 and a flue gas treatment system 2, and the waste organic salt treatment system 1 includes a
净化工业废盐经热力窑102的窑尾1024后,进入中间仓103,中间仓103的净化工业废盐通过变频的回流输送系统和进料仓101连接,净化工业废盐可以通过回流输送系统,循环进入进料仓101,和进料仓101中未经过处理的工业废盐混合,一起再进入热力窑102。通过回流输送系统频率的改变,可以调整循环工业废盐量。Purified industrial waste salt passes through the
借助净化工业废盐和未净化工业废盐的混合,可以起到如下作用:With the help of the mixture of purified industrial waste salt and unpurified industrial waste salt, it can play the following roles:
a、可以减少工业废盐在进料仓101中的黏结和堵塞现象;a. It can reduce the cohesion and clogging of industrial waste salt in the
b、减少工业废盐在热力窑102中的结块现象;b, reduce the agglomeration of industrial waste salt in the
c、强化传热过程,回收一部分热量。c. Strengthen the heat transfer process and recover part of the heat.
进一步的,烟气处理系统2包括除尘器201、燃烧室202、烟气净化装置203以及循环风机204,除尘器201与热力窑102连接并连通,除尘器201、燃烧室202、烟气净化装置203以及循环风机204顺次首尾相接,烟气从热力窑102排出先后经过除尘器201除尘,燃烧室202燃烧以及烟气净化装置203净化后,通过循环风机204循环至热力窑102。Further, the flue gas treatment system 2 includes a
还包括引风机205和烟囱206,引风机205同时与烟囱206和烟气净化装置203连接,引风机205用于向外排放经过烟气净化装置203净化后的达标烟气。It also includes an induced
具体的,从热力窑102出来的烟气,进入除尘器201,把烟气中可能携带的盐分离出来。Specifically, the flue gas from the
需要说明的是,本发明的燃烧室202为沉降式燃烧室,除尘器201出来的烟气进入燃烧室202,升温至1100℃,并在1100℃温度区间停留2s,保证热力窑102中热解产生的气体化合物完全无害化分解;燃烧室202采用天然气加热,通过天然气流量的调节,控制燃烧温度,通过新鲜风量的调节,控制烟气中的氧含量。It should be noted that the
燃烧室202产生的烟气,进入烟气净化装置203,而烟气净化装置203则包括:半干法急冷脱酸塔、SNCR、布袋除尘器201、烟气冷凝器和烟气换热器,经烟气换热器换热后,进入引风机205或循环风机204的烟气温度为200℃,即烟气净化装置203后的烟气分两路,一路经循环风机204进入热力窑102,实现烟气的再循环,另一路达标后经引风机205和烟囱206向外排放,经烟囱206排放的烟气,其排放指标满足《GB18484 危险废物焚烧污染控制标准》的要求。The flue gas produced by the
其中,冷凝器可降低循环烟气中的水蒸气含量。Among them, the condenser can reduce the water vapor content in the circulating flue gas.
进一步的,热力窑102上安装电加热器1023,电加热器1023分为三个独立回路,如图2所示,用于控制热力窑102的温度,即通过三个独立回路分别控制温度,温度控制精度为±5℃。Further, an
进一步的,热力窑102的窑头处设置加湿水雾化喷枪和水流量控制回路,根据实际有机物废盐中的有机物去除效果,用于控制热力窑102的水量。Further, the kiln head of the
进一步的,热力窑102的窑头处设置氮气喷头和氮气流量控制回路,根据实际有机物废盐中的有机物去除效果,用于控制热力窑102的氮气量。Further, the kiln head of the
以上所述,仅为本发明的具体实施方式,但本发明的保护范围并不局限于此,任何熟悉本技术领域的技术人员在本发明揭露的技术范围内,可轻易想到变化或替换,都应涵盖在本发明的保护范围之内。因此,本发明的保护范围应以所述权利要求的保护范围为准。The above is only a specific embodiment of the present invention, but the scope of protection of the present invention is not limited thereto. Anyone skilled in the art can easily think of changes or substitutions within the technical scope disclosed in the present invention. Should be covered within the protection scope of the present invention. Therefore, the protection scope of the present invention should be determined by the protection scope of the claims.
Claims (7)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202011377335.7A CN112404110B (en) | 2020-11-30 | 2020-11-30 | Method and system for treating waste salt containing organic matter using double-cycle thermal purification technology |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202011377335.7A CN112404110B (en) | 2020-11-30 | 2020-11-30 | Method and system for treating waste salt containing organic matter using double-cycle thermal purification technology |
Publications (2)
Publication Number | Publication Date |
---|---|
CN112404110A CN112404110A (en) | 2021-02-26 |
CN112404110B true CN112404110B (en) | 2023-07-14 |
Family
ID=74829053
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202011377335.7A Active CN112404110B (en) | 2020-11-30 | 2020-11-30 | Method and system for treating waste salt containing organic matter using double-cycle thermal purification technology |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN112404110B (en) |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107321755A (en) * | 2017-06-30 | 2017-11-07 | 江苏省环境科学研究院 | A kind of abraum salt process for reclaiming and its special purpose device |
CN206911924U (en) * | 2017-06-30 | 2018-01-23 | 江苏省环境科学研究院 | Process unit for abraum salt recycling |
CN207238730U (en) * | 2017-07-27 | 2018-04-17 | 重庆盎瑞悦科技有限公司 | Reclaimer is burned in a kind of negative-pressure cyclic accumulation of heat that harmlessness disposing is carried out to high saliferous chemical engineering sludge |
CN110642271A (en) * | 2019-10-31 | 2020-01-03 | 江苏省环境科学研究院 | Device and method for melting treatment and refining of industrial waste salt |
CN110805907A (en) * | 2019-10-16 | 2020-02-18 | 北京航化节能环保技术有限公司 | Process and device for treating solid waste salt cracking furnace containing water, organic matters and other soluble gases |
Family Cites Families (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
AUPN644895A0 (en) * | 1995-11-08 | 1995-11-30 | Miltox Holdings Pte Ltd | Method and apparatus for waste treatment |
-
2020
- 2020-11-30 CN CN202011377335.7A patent/CN112404110B/en active Active
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107321755A (en) * | 2017-06-30 | 2017-11-07 | 江苏省环境科学研究院 | A kind of abraum salt process for reclaiming and its special purpose device |
CN206911924U (en) * | 2017-06-30 | 2018-01-23 | 江苏省环境科学研究院 | Process unit for abraum salt recycling |
CN207238730U (en) * | 2017-07-27 | 2018-04-17 | 重庆盎瑞悦科技有限公司 | Reclaimer is burned in a kind of negative-pressure cyclic accumulation of heat that harmlessness disposing is carried out to high saliferous chemical engineering sludge |
CN110805907A (en) * | 2019-10-16 | 2020-02-18 | 北京航化节能环保技术有限公司 | Process and device for treating solid waste salt cracking furnace containing water, organic matters and other soluble gases |
CN110642271A (en) * | 2019-10-31 | 2020-01-03 | 江苏省环境科学研究院 | Device and method for melting treatment and refining of industrial waste salt |
Also Published As
Publication number | Publication date |
---|---|
CN112404110A (en) | 2021-02-26 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN107642786B (en) | System and process for cooperatively disposing hazardous waste in ceramsite production | |
CN208162277U (en) | A kind of thermal desorption system of contaminated soil | |
CN103145307A (en) | High temperature carbonization system of sludge and carbonization process | |
CN110759626A (en) | Sludge conditioning dehydration coupling carbonization reduction treatment method and system | |
CN104874593A (en) | Method and device for treating organic polluted soil by two-section-type indirect thermal desorption technology | |
CN110107902A (en) | Method for integrated treatment of chemical waste salt by oxygen-containing thermal desorption and catalytic oxidation | |
CN103420549A (en) | Harmless waste treatment method in coal chemical industry | |
CN113843264B (en) | Method and system for microwave thermal desorption and oxidation treatment of waste salt | |
CN105948150A (en) | Process and system for recycling high-chloride high-concentration non-degradable organic wastewater | |
CN108640458A (en) | Greasy filth innoxious thermal desorption processing system and processing method | |
CN110394351A (en) | A short process method and system for degrading dioxins in fly ash | |
CN112404110B (en) | Method and system for treating waste salt containing organic matter using double-cycle thermal purification technology | |
CN107639110B (en) | Device for repairing contaminated soil | |
CN206911924U (en) | Process unit for abraum salt recycling | |
CN110043909A (en) | A kind of chemical engineering sludge burning process | |
CN212404016U (en) | Waste salt vacuum cracking system | |
CN111978966A (en) | Oily sludge treatment system based on syllogic rotary kiln | |
CN1556349A (en) | Domestic garbage treatment and cement rotary kiln combined production technology | |
CN1673099A (en) | Method of treating organic waste water containing salt | |
CN208586189U (en) | The innoxious thermal desorption processing system of greasy filth | |
CN217275479U (en) | Waste salt pyrolysis treatment system based on multi-hearth furnace | |
CN114405968B (en) | An in-situ oxidation hazardous waste disposal system | |
CN215626892U (en) | High organic waste water of containing salt deals with device | |
CN211232880U (en) | High, low calorific value hazardous waste burns melting innocent treatment system in coordination | |
CN101200646B (en) | Waste water zero discharging method for coke-oven gas dew-point returning process |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
TA01 | Transfer of patent application right |
Effective date of registration: 20230625 Address after: 450m east of Yanglinshui Village, Shijiaying Township, Fangshan District, Beijing 102461 Applicant after: Beijing Aerospace Shengyong Chemical Equipment Co.,Ltd. Address before: 117000 No.22, unit 2, 9-7, Fenghua new town, No.5 Digong Road, Mingshan District, Benxi City, Liaoning Province Applicant before: Sun Lifeng |
|
TA01 | Transfer of patent application right | ||
GR01 | Patent grant | ||
GR01 | Patent grant |