CN114904381A - A kind of cement production system and its gas treatment method - Google Patents
A kind of cement production system and its gas treatment method Download PDFInfo
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Abstract
本发明提供了一种水泥生产系统及其气体处理方法。水泥生产系统包括顺序气体连接的水泥分解和高温脱硝单元、生料磨、除尘单元、低温脱硝单元和湿法处理单元。气体处理方法包括:在每个生产周期中,根据生料磨的运行状态,使水泥分解和高温脱硝单元的排出气体依次经过或不经过生料磨进行热交换、经过除尘单元进行除尘和经过低温脱硝单元进行选择性催化还原脱硝处理后,根据预设规则使处理后的排出气体经过湿法处理单元进行湿法吸收得到回收浆液;将回收浆液作为脱硝还原剂回用至水泥分解和高温脱硝单元或低温脱硝单元。延长低温催化催化剂的寿命,保证脱硝效率,降低氨逃逸,并有效降低脱硝还原剂的消耗从而降低脱硝成本。
The present invention provides a cement production system and a gas treatment method thereof. The cement production system includes sequential gas connected cement decomposition and high temperature denitration unit, raw meal mill, dust removal unit, low temperature denitration unit and wet processing unit. The gas treatment method includes: in each production cycle, according to the operating state of the raw meal mill, the exhaust gas from the cement decomposition and high temperature denitration unit passes through or does not pass through the raw meal mill for heat exchange, passes through the dust removal unit for dedusting, and passes through the low temperature denitrification unit. After the selective catalytic reduction and denitration treatment in the denitration unit, the treated exhaust gas is subjected to wet absorption by the wet treatment unit according to preset rules to obtain recovered slurry; the recovered slurry is reused as a denitration reducing agent to the cement decomposition and high temperature denitration unit or low temperature denitration unit. Extend the life of the low-temperature catalytic catalyst, ensure the denitration efficiency, reduce the escape of ammonia, and effectively reduce the consumption of denitration reducing agents, thereby reducing the cost of denitration.
Description
技术领域technical field
本发明涉及气体处理技术领域,特别是一种水泥生产系统及其气体处理方法。The invention relates to the technical field of gas treatment, in particular to a cement production system and a gas treatment method thereof.
背景技术Background technique
在水泥生产的高温煅烧、燃料煤燃烧以及生料分解等过程中会产生大量的氮氧化物(NOx)。随着环保要求日益严格,氮氧化物(NOx)的排放限值越来越低。为达到排放限值的要求,在对含氮氧化物的排气进行脱硝时,脱硝还原剂(如氨水、尿素、三聚氰胺等含氮物质)的喷入量越来越大,不仅引起成本上升,而且导致氨逃逸问题也越来越严重。氨逃逸不仅会污染大气,影响人体健康,也增大了脱硝还原剂的消耗,增加了成本。而且,传统的水泥窑进行排气脱硝时,将脱硝催化剂布置在生料磨之前的高温、高尘段,导致催化剂的寿命极短,同时容易被尘堵塞导致停产。Large amounts of nitrogen oxides (NOx) are produced during high-temperature calcination in cement production, fuel coal combustion, and raw meal decomposition. With increasingly stringent environmental protection requirements, the emission limits for nitrogen oxides (NOx) are getting lower and lower. In order to meet the requirements of emission limits, when denitrifying exhaust gas containing nitrogen oxides, the injection of denitration reducing agents (such as ammonia, urea, melamine and other nitrogen-containing substances) is increasing, which not only causes costs to rise, but also And the problem of ammonia escape is getting more and more serious. Ammonia escape not only pollutes the atmosphere and affects human health, but also increases the consumption of denitration reducing agents and increases costs. Moreover, when the traditional cement kiln conducts exhaust gas denitrification, the denitration catalyst is arranged in the high temperature and high dust section before the raw meal mill, resulting in a very short lifespan of the catalyst, and at the same time, it is easy to be blocked by dust and lead to production stoppage.
发明内容SUMMARY OF THE INVENTION
鉴于上述问题,本发明提供一种克服上述问题或者至少部分地解决上述问题的水泥生产系统及其气体处理方法。In view of the above problems, the present invention provides a cement production system and a gas treatment method thereof that overcome the above problems or at least partially solve the above problems.
本发明的一个目的在于提供一种有效降低脱硝还原剂的消耗从而降低脱硝成本的水泥生产系统的气体处理方法。An object of the present invention is to provide a gas treatment method for a cement production system that can effectively reduce the consumption of denitration reducing agent and thereby reduce the cost of denitration.
本发明的一个进一步的目的在于通过合理设置每个生产周期中生料磨和湿法处理单元的开启时间,在保证脱硝效果的前提下,降低整个系统的运行成本。A further object of the present invention is to reduce the operating cost of the entire system under the premise of ensuring the denitrification effect by reasonably setting the start-up time of the raw meal mill and the wet processing unit in each production cycle.
本发明的又一个进一步的目的在于提高回收浆液的稳定性。Yet another further object of the present invention is to improve the stability of the recovered slurry.
本发明的又一个进一步的目的在于提高脱硝催化剂的使用寿命。Yet another further object of the present invention is to improve the service life of the denitration catalyst.
本发明的又一个进一步的目的在于降低催化剂堵塞的风险。Yet a further object of the present invention is to reduce the risk of catalyst plugging.
本发明的又一个进一步的目的在于对烟气进行脱硫。Yet another further object of the present invention is to desulfurize flue gas.
本发明的另一个目的在于提供一种可实现上述气体处理方法的水泥生产系统。Another object of the present invention is to provide a cement production system capable of realizing the above-mentioned gas treatment method.
特别地,根据本发明实施例的一方面,提供了一种水泥生产系统的气体处理方法,所述水泥生产系统包括顺序气体连接的水泥分解和高温脱硝单元、生料磨、除尘单元、低温脱硝单元和湿法处理单元,所述气体处理方法包括:In particular, according to an aspect of the embodiments of the present invention, there is provided a gas treatment method for a cement production system, the cement production system comprising a cement decomposition and high temperature denitration unit, a raw meal mill, a dust removal unit, and a low temperature denitration unit connected by sequential gas unit and wet processing unit, the gas processing method comprises:
在每个生产周期中,根据所述生料磨的运行状态,使所述水泥分解和高温脱硝单元的排出气体依次经过或不经过所述生料磨进行热交换、经过所述除尘单元进行除尘和经过所述低温脱硝单元进行选择性催化还原脱硝处理后,根据预设规则使处理后的所述排出气体经过所述湿法处理单元进行湿法吸收得到回收浆液;In each production cycle, according to the operating state of the raw meal mill, the exhaust gas from the cement decomposition and high-temperature denitration unit is made to pass through or not pass through the raw meal mill for heat exchange, and pass through the dust removal unit for dedusting. and after the selective catalytic reduction and denitration treatment is performed by the low-temperature denitration unit, the treated exhaust gas is subjected to wet absorption through the wet treatment unit according to preset rules to obtain a recovered slurry;
将所述回收浆液作为脱硝还原剂回用至所述水泥分解和高温脱硝单元或所述低温脱硝单元。The recovered slurry is reused as a denitration reducing agent to the cement decomposition and high temperature denitration unit or the low temperature denitration unit.
可选地,所述生料磨的运行状态包括开启状态和关闭状态;且Optionally, the operating state of the raw meal mill includes an open state and a closed state; and
在每个生产周期中,当所述生料磨的运行状态为所述开启状态时,使所述水泥分解和高温脱硝单元的排出气体经过所述生料磨进行热交换,当所述生料磨的运行状态为所述关闭状态时,使所述水泥分解和高温脱硝单元的排出气体不经过所述生料磨进行热交换。In each production cycle, when the operating state of the raw meal mill is the open state, the exhaust gas of the cement decomposition and high temperature denitration unit is passed through the raw meal mill for heat exchange. When the running state of the mill is the closed state, the exhaust gas of the cement decomposition and high temperature denitration unit is not subjected to heat exchange through the raw meal mill.
可选地,所述预设规则包括无论所述生料磨的运行状态是否为所述开启状态均开启所述湿法处理单元;并且Optionally, the preset rule includes turning on the wet processing unit regardless of whether the operating state of the raw meal mill is the on state; and
所述根据预设规则使处理后的所述排出气体经过所述湿法处理单元进行湿法吸收得到回收浆液的步骤包括:The step of making the treated exhaust gas pass through the wet processing unit for wet absorption to obtain recovered slurry according to a preset rule includes:
无论所述生料磨的运行状态是否为所述开启状态均使处理后的所述排出气体经过所述湿法处理单元进行湿法吸收得到所述回收浆液。Regardless of whether the operating state of the raw meal mill is the open state, the treated exhaust gas is subjected to wet absorption through the wet process unit to obtain the recovered slurry.
可选地,所述预设规则包括当所述生料磨的运行状态是所述开启状态时,关闭所述湿法处理单元,当所述生料磨的运行状态是所述关闭状态时,开启所述湿法处理单元;并且Optionally, the preset rule includes closing the wet processing unit when the operation state of the raw meal mill is the open state, and when the operation state of the raw meal mill is the closed state, turning on the wet processing unit; and
所述根据预设规则使处理后的所述排出气体经过所述湿法处理单元进行湿法吸收得到回收浆液的步骤包括:The step of making the treated exhaust gas pass through the wet processing unit for wet absorption to obtain recovered slurry according to a preset rule includes:
当所述生料磨的运行状态是所述开启状态时,关闭所述湿法处理单元,使处理后的所述排出气体不经过所述湿法处理单元;When the running state of the raw meal mill is the open state, closing the wet processing unit, so that the treated exhaust gas does not pass through the wet processing unit;
当所述生料磨的运行状态是所述关闭状态时,开启所述湿法处理单元,并使处理后的所述排出气体经过所述湿法处理单元进行湿法吸收得到所述回收浆液。When the operating state of the raw meal mill is the closed state, the wet processing unit is turned on, and the treated exhaust gas is subjected to wet absorption through the wet processing unit to obtain the recovered slurry.
可选地,将所述低温脱硝单元配置为使得当所述生料磨的运行状态是所述开启状态时,所述低温脱硝单元中的脱硝催化剂在所述选择性催化还原脱硝处理中吸附并存储所述排出气体中携带的氨,并且然后当所述生料磨的运行状态是所述关闭状态时,允许存储于所述脱硝催化剂内的氨与氮氧化物发生反应;Optionally, the low temperature denitrification unit is configured such that when the operating state of the raw meal mill is the open state, the denitration catalyst in the low temperature denitration unit is adsorbed and adsorbed in the selective catalytic reduction denitration treatment. storing ammonia entrained in the exhaust gas and then allowing the ammonia stored in the denitration catalyst to react with nitrogen oxides when the operating state of the green mill is the off state;
优选地,所述低温脱硝单元的所述脱销催化剂为抗硫催化剂。Preferably, the destocking catalyst of the low temperature denitration unit is an anti-sulfur catalyst.
可选地,在每个所述生产周期中,所述生料磨处于所述开启状态的时间占比大于或等于70%且小于100%;Optionally, in each production cycle, the proportion of time when the raw meal mill is in the open state is greater than or equal to 70% and less than 100%;
优选地,在每个所述生产周期中,所述生料磨处于所述开启状态的时间占比为80%。Preferably, in each production cycle, the proportion of time that the raw meal mill is in the open state is 80%.
可选地,所述回收浆液中包含的物质至少包括铵盐,且以氨基量计,所述铵盐的摩尔数量占所述回收浆液中包含的所有氨类物质的总摩尔数量的50%以上。Optionally, the substances contained in the recovered slurry include at least ammonium salts, and in terms of the amount of amino groups, the molar amount of the ammonium salts accounts for more than 50% of the total molar amount of all ammonia substances contained in the recovered slurry. .
可选地,所述湿法处理单元中所用的吸收液包括以下至少之一:水、稀硫酸和稀亚硫酸;且Optionally, the absorbing liquid used in the wet processing unit includes at least one of the following: water, dilute sulfuric acid and dilute sulfurous acid; and
所述铵盐包括下列至少之一:硫酸铵、硫酸氢铵、亚硫酸铵和亚硫酸氢铵。The ammonium salt includes at least one of the following: ammonium sulfate, ammonium bisulfite, ammonium sulfite, and ammonium bisulfite.
根据本发明实施例的另一方面,还提供了一种水泥生产系统,包括顺序气体连接的水泥分解和高温脱硝单元、生料磨、除尘单元、低温脱硝单元和湿法处理单元,其中,在每个生产周期中,According to another aspect of the embodiments of the present invention, there is also provided a cement production system, comprising a cement decomposition and high temperature denitration unit, a raw meal mill, a dedusting unit, a low temperature denitration unit and a wet process unit connected in sequence gas, wherein the During each production cycle,
所述水泥分解和高温脱硝单元配置为对预处理后的水泥生料进行分解,并对气流中的氮氧化物进行选择性非催化还原脱硝处理;The cement decomposition and high temperature denitration unit is configured to decompose the pretreated cement raw meal, and to perform selective non-catalytic reduction and denitration treatment on nitrogen oxides in the gas stream;
所述生料磨配置为根据自身的运行状态与所述水泥分解和高温脱硝单元的排出气体进行或不进行热交换;The raw meal mill is configured to perform or not to perform heat exchange with the exhaust gas of the cement decomposition and high temperature denitration unit according to its own operating state;
所述除尘单元配置为对已进行所述热交换或未进行所述热交换的所述排出气体进行除尘;The dedusting unit is configured to dedust the exhaust gas that has undergone the heat exchange or has not undergone the heat exchange;
所述低温脱硝单元配置为对除尘后的所述排出气体进行选择性催化还原脱硝处理;The low-temperature denitration unit is configured to perform selective catalytic reduction and denitration treatment on the dedusted exhaust gas;
所述湿法处理单元配置为根据预设规则对经过所述选择性催化还原脱硝处理后的所述排出气体进行湿法吸收得到回收浆液,并将所述回收浆液作为脱硝还原剂返回至所述水泥分解和高温脱硝单元或所述低温脱硝单元。The wet processing unit is configured to perform wet absorption on the exhaust gas after the selective catalytic reduction and denitration treatment according to preset rules to obtain a recovered slurry, and return the recovered slurry as a denitration reducing agent to the Cement decomposition and high temperature denitration unit or said low temperature denitration unit.
可选地,所述生料磨的运行状态包括开启状态和关闭状态;且Optionally, the operating state of the raw meal mill includes an open state and a closed state; and
所述生料磨还配置为:The raw meal mill is also configured as:
当所述生料磨的运行状态为所述开启状态时,与所述排出气体进行热交换,当所述生料磨的运行状态为所述关闭状态时,不与所述排出气体进行热交换。When the operating state of the raw meal mill is the open state, heat exchange is performed with the exhaust gas, and when the operation state of the raw meal mill is the closed state, heat exchange is not performed with the exhaust gas .
可选地,所述预设规则包括无论所述生料磨的运行状态是否为所述开启状态所述湿法处理单元均开启;并且Optionally, the preset rule includes that the wet processing unit is turned on regardless of whether the operating state of the raw meal mill is the on state; and
所述湿法处理单元还配置为:The wet processing unit is further configured to:
无论所述生料磨的运行状态是否为所述开启状态均保持开启并对经过所述选择性催化还原脱硝处理后的所述排出气体进行湿法吸收得到所述回收浆液。Regardless of whether the operating state of the raw meal mill is the open state, it remains open and wet absorption is performed on the exhaust gas after the selective catalytic reduction and denitration treatment to obtain the recovered slurry.
可选地,所述预设规则包括当所述生料磨的运行状态是所述开启状态时,所述湿法处理单元关闭,当所述生料磨的运行状态是所述关闭状态时,所述湿法处理单元开启;并且Optionally, the preset rule includes that when the running state of the raw meal mill is the open state, the wet processing unit is closed, and when the running state of the raw meal mill is the closed state, the wet processing unit is turned on; and
所述湿法处理单元还配置为:The wet processing unit is further configured to:
当所述生料磨的运行状态是所述开启状态时,所述湿法处理单元关闭以不对所述排出气体进行湿法吸收;When the operating state of the raw meal mill is the open state, the wet processing unit is turned off so as not to wet absorb the exhaust gas;
当所述生料磨的运行状态是所述关闭状态时,所述湿法处理单元开启,并对所述排出气体进行湿法吸收得到所述回收浆液。When the operating state of the raw meal mill is the closed state, the wet processing unit is turned on, and wet absorption is performed on the exhaust gas to obtain the recovered slurry.
可选地,所述低温脱硝单元还被配置为:当所述生料磨的运行状态是所述开启状态时,所述低温脱硝单元中的脱硝催化剂在所述选择性催化还原脱硝处理中吸附并存储所述排出气体中携带的氨,并且然后当所述生料磨的运行状态是所述关闭状态时,允许存储于所述脱硝催化剂内的氨与氮氧化物发生反应。Optionally, the low temperature denitration unit is further configured to: when the operating state of the raw meal mill is the open state, the denitration catalyst in the low temperature denitration unit is adsorbed in the selective catalytic reduction denitration treatment And the ammonia carried in the exhaust gas is stored, and then the ammonia stored in the denitration catalyst is allowed to react with nitrogen oxides when the operating state of the raw mill is the closed state.
可选地,在每个所述生产周期中,所述生料磨处于所述开启状态的时间占比大于或等于70%且小于100%;Optionally, in each production cycle, the proportion of time when the raw meal mill is in the open state is greater than or equal to 70% and less than 100%;
优选地,在每个所述生产周期中,所述生料磨处于所述开启状态的时间占比为80%。Preferably, in each production cycle, the proportion of time that the raw meal mill is in the open state is 80%.
可选地,所述回收浆液中包含的物质至少包括铵盐,且以氨基量计,所述铵盐的摩尔数量占所述回收浆液中包含的所有氨类物质的总摩尔数量的50%以上;Optionally, the substances contained in the recovered slurry include at least ammonium salts, and in terms of the amount of amino groups, the molar amount of the ammonium salts accounts for more than 50% of the total molar amount of all ammonia substances contained in the recovered slurry. ;
所述湿法处理单元中所用的吸收液以下至少之一:水、稀硫酸和稀亚硫酸;且The absorption liquid used in the wet processing unit is at least one of the following: water, dilute sulfuric acid and dilute sulfurous acid; and
所述铵盐包括下列至少之一:硫酸铵、硫酸氢铵、亚硫酸铵和亚硫酸氢铵。The ammonium salt includes at least one of the following: ammonium sulfate, ammonium bisulfite, ammonium sulfite, and ammonium bisulfite.
本发明的水泥生产系统及其气体处理方法中,将低温催化脱硝工序布置在生料磨和除尘单元之后,并在低温催化脱硝工序之后布置湿法处理单元,其根据预设规则开启以用于吸收排出气体中携带的逃逸的二氧化硫、三氧化硫、硫酸盐、氨和铵盐等,并将吸收后的废液作为还原剂回用到高温SNCR脱硝或低温SCR脱硝。这延长了低温催化脱硝工序中的催化剂的寿命,保证了脱硝效率,降低了氨逃逸,有效降低了脱硝还原剂的消耗从而降低脱硝成本。In the cement production system and the gas treatment method thereof of the present invention, the low-temperature catalytic denitrification process is arranged after the raw meal mill and the dust removal unit, and the wet process unit is arranged after the low-temperature catalytic denitration process, which is turned on according to preset rules for use in Absorb the escaped sulfur dioxide, sulfur trioxide, sulfate, ammonia and ammonium salts carried in the exhaust gas, and reuse the absorbed waste liquid as a reducing agent for high-temperature SNCR denitration or low-temperature SCR denitration. This prolongs the life of the catalyst in the low-temperature catalytic denitration process, ensures the denitration efficiency, reduces the escape of ammonia, effectively reduces the consumption of the denitration reducing agent, and thus reduces the denitration cost.
进一步地,本发明的水泥生产系统及其气体处理方法中,在每个生产周期中,生料磨的运行状态包括开启状态和关闭状态。当生料磨处于开启状态时,其内的生料与来自水泥分解和高温脱硝单元的排出气体进行热交换,并且湿法处理单元关闭,氨逃逸由低温脱硝单元吸附。当生料磨处于关闭状态时,则其内的生料不与该排出气体进行热交换,低温脱硝单元可以在较高的温度下与氮氧化物充分反应,并且湿法处理单元开启,以对经低温催化脱硝工序之后的排出气体进行湿法吸收得到回收浆液。这样,通过合理设置每个生产周期中生料磨和湿法处理单元的开启时间,能够在保证脱硝效果的前提下,降低整个系统的运行成本。Further, in the cement production system and the gas treatment method thereof of the present invention, in each production cycle, the operation state of the raw meal mill includes an open state and a closed state. When the raw meal mill is in the open state, the raw meal in it exchanges heat with the exhaust gas from the cement decomposition and high temperature denitration unit, and the wet processing unit is closed, and the ammonia escape is adsorbed by the low temperature denitration unit. When the raw meal mill is in a closed state, the raw meal in it does not exchange heat with the exhaust gas, the low-temperature denitration unit can fully react with nitrogen oxides at a higher temperature, and the wet processing unit is turned on to The exhaust gas after the low-temperature catalytic denitration process is subjected to wet absorption to obtain a recovered slurry. In this way, by reasonably setting the start-up time of the raw meal mill and the wet processing unit in each production cycle, the operating cost of the entire system can be reduced on the premise of ensuring the denitration effect.
进一步地,本发明的水泥生产系统及其气体处理方法中,所得到的回收浆液中所包含的物质以铵盐为主,浆液更稳定,不易形成二次氨逃逸。Further, in the cement production system and the gas treatment method thereof of the present invention, the substances contained in the recovered slurry are mainly ammonium salts, and the slurry is more stable, and it is not easy to form secondary ammonia escape.
上述说明仅是本发明技术方案的概述,为了能够更清楚了解本发明的技术手段,而可依照说明书的内容予以实施,并且为了让本发明的上述和其它目的、特征和优点能够更明显易懂,以下特举本发明的具体实施方式。The above description is only an overview of the technical solutions of the present invention, in order to be able to understand the technical means of the present invention more clearly, it can be implemented according to the content of the description, and in order to make the above and other purposes, features and advantages of the present invention more obvious and easy to understand , the following specific embodiments of the present invention are given.
根据下文结合附图对本发明具体实施例的详细描述,本领域技术人员将会更加明了本发明的上述以及其他目的、优点和特征。The above and other objects, advantages and features of the present invention will be more apparent to those skilled in the art from the following detailed description of the specific embodiments of the present invention in conjunction with the accompanying drawings.
附图说明Description of drawings
通过阅读下文优选实施方式的详细描述,各种其他的优点和益处对于本领域普通技术人员将变得清楚明了。附图仅用于示出优选实施方式的目的,而并不认为是对本发明的限制。而且在整个附图中,用相同的参考符号表示相同的部件。在附图中:Various other advantages and benefits will become apparent to those of ordinary skill in the art upon reading the following detailed description of the preferred embodiments. The drawings are for the purpose of illustrating preferred embodiments only and are not to be considered limiting of the invention. Also, the same components are denoted by the same reference numerals throughout the drawings. In the attached image:
图1示出了根据本发明一实施例的水泥生产系统的示意性结构框图;Fig. 1 shows a schematic structural block diagram of a cement production system according to an embodiment of the present invention;
图2示出了根据本发明一实施例的水泥生产系统的气体处理方法的流程示意图;FIG. 2 shows a schematic flowchart of a gas treatment method for a cement production system according to an embodiment of the present invention;
图3示出了根据本发明另一实施例的水泥生产系统的气体处理方法的流程示意图。FIG. 3 shows a schematic flowchart of a gas treatment method of a cement production system according to another embodiment of the present invention.
具体实施方式Detailed ways
下面将参照附图更详细地描述本公开的示例性实施例。虽然附图中显示了本公开的示例性实施例,然而应当理解,可以以各种形式实现本公开而不应被这里阐述的实施例所限制。相反,提供这些实施例是为了能够更透彻地理解本公开,并且能够将本公开的范围完整的传达给本领域的技术人员。Exemplary embodiments of the present disclosure will be described in more detail below with reference to the accompanying drawings. While exemplary embodiments of the present disclosure are shown in the drawings, it should be understood that the present disclosure may be embodied in various forms and should not be limited by the embodiments set forth herein. Rather, these embodiments are provided so that the present disclosure will be more thoroughly understood, and will fully convey the scope of the present disclosure to those skilled in the art.
为解决上述技术问题,本发明提供了一种水泥生产系统。In order to solve the above technical problems, the present invention provides a cement production system.
图1示出了根据本发明一实施例的水泥生产系统100的示意性结构框图。参见图1所示,水泥生产系统100至少可以包括顺序气体连接的水泥分解和高温脱硝单元110、生料磨120、除尘单元130、低温脱硝单元140和湿法处理单元150。此处提及的顺序气体连接可以理解为每一在前的单元的气体出口与相邻的在后单元的气体进口相连。需要说明的是,图1中带箭头的实线表示气体通道,带箭头的虚线表示作为脱硝还原剂的物质自湿法处理单元150返回至水泥分解和高温脱硝单元110或低温脱硝单元140的回用传输通道,带箭头的点划线则表示自生料磨120至水泥分解和高温脱硝单元110的生料传输通道。FIG. 1 shows a schematic structural block diagram of a
在每个生产周期中,水泥分解和高温脱硝单元110配置为对预处理后的水泥生料进行分解,并对气流中的氮氧化物进行选择性非催化还原(Selective Non-CatalyticReduction,简称为SNCR)脱硝处理。具体地,在SNCR脱硝处理中喷入还原剂,如氨水、尿素、三聚氰胺等含氮物质。水泥生料分解及相应的SNCR脱硝处理的具体操作应为本领域技术人员所习知,本文不再详细介绍。In each production cycle, the cement decomposition and high temperature denitration unit 110 is configured to decompose the pretreated cement raw meal, and to perform Selective Non-Catalytic Reduction (SNCR for short) on nitrogen oxides in the gas stream ) denitrification treatment. Specifically, reducing agents such as ammonia, urea, melamine and other nitrogen-containing substances are sprayed in the SNCR denitration treatment. The specific operations of the decomposition of the cement raw meal and the corresponding SNCR denitration treatment should be known to those skilled in the art, and will not be described in detail herein.
生料磨120配置为根据自身的运行状态与水泥分解和高温脱硝单元110的排出气体进行或不进行热交换。具体地,在生料磨120中可以使该排出气体通过预热器对生料进行预加热。当然,也可以通过其他方式使排出气体与生料进行热交换,本发明对此不做限制。生料磨120中处理后的生料通过生料传输通道输送至水泥分解和高温脱硝单元110。The
除尘单元130配置为对已进行热交换或未进行热交换的排出气体进行除尘。具体地,除尘单元130可采用布袋除尘器等。The
低温脱硝单元140配置为对除尘后的排出气体进行选择性催化还原(SelectiveCatalytic Reduction,简称为SCR)脱硝处理。具体地,低温脱硝单元140中可设置低温脱硝催化剂,通过喷入还原剂,在120℃至200℃的温度,优选120℃至180℃的温度,例如130℃、140℃、150℃、160℃、170℃温度下,进行选择性催化还原反应。低温脱硝催化剂可采用当前市面上可得的低温脱硝催化剂,当然也可以采用其他的低温脱硝催化剂,优选具备抗硫能力的催化剂,本发明对此不做限制。The low temperature denitration unit 140 is configured to perform selective catalytic reduction (Selective Catalytic Reduction, SCR for short) denitration treatment on the dedusted exhaust gas. Specifically, a low-temperature denitration catalyst can be set in the low-temperature denitration unit 140, and by spraying a reducing agent, at a temperature of 120°C to 200°C, preferably a temperature of 120°C to 180°C, such as 130°C, 140°C, 150°C, 160°C , 170 ℃ temperature, the selective catalytic reduction reaction. The low-temperature denitration catalyst can be a low-temperature denitration catalyst currently available on the market, and of course other low-temperature denitration catalysts can also be used, preferably a catalyst with sulfur resistance, which is not limited in the present invention.
湿法处理单元150配置为根据预设规则对经过选择性催化还原脱硝处理后的排出气体进行湿法吸收得到回收浆液,并将回收浆液作为脱硝还原剂返回至水泥分解和高温脱硝单元110。具体地,在湿法处理单元150中使该排出气体与吸收液接触进行湿法吸收,从而通过吸收液吸收排出气体中携带的逃逸的二氧化硫、三氧化硫、硫酸盐、氨和铵盐等。吸收液可以包括水,也可以用酸性溶液(例如稀硫酸、稀亚硫酸等),以提高氨和铵盐等氨类物质的吸收效果。得到的回收浆液通过回用传输通道输送至水泥分解和高温脱硝单元110或者低温脱硝单元140。The
由于回收浆液中富含氨类还原性物质,在一些实施方案中,可以将回收浆液直接喷入水泥分解和高温脱硝单元110(如分解炉及其附近工段),实现SNCR脱硝。在另一些可替换的实施方案中,也可以先在回收浆液中加入碱性物质(如碳酸氢钠等),使其与铵盐反应生成氨气,再将氨气喷入水泥分解和高温脱硝单元110,实现SNCR脱硝。回收浆液回用至低温脱硝单元140时,方式与水泥分解和高温脱硝单元110类似,不再赘述。Since the recovered slurry is rich in ammonia-based reducing substances, in some embodiments, the recovered slurry can be directly sprayed into the cement decomposition and high-temperature denitration unit 110 (eg, a decomposition furnace and its adjacent sections) to achieve SNCR denitration. In other alternative embodiments, alkaline substances (such as sodium bicarbonate, etc.) can also be added to the recovered slurry to react with ammonium salts to generate ammonia gas, and then the ammonia gas is sprayed into the cement for decomposition and high-temperature denitration. Unit 110, realizes SNCR denitration. When the recovered slurry is reused to the low temperature denitration unit 140, the method is similar to that of the cement decomposition and high temperature denitration unit 110, and will not be repeated here.
本发明实施例的水泥生产系统100中,将低温脱硝单元140布置在生料磨120和除尘单元130之后,并在低温脱硝单元140之后布置湿法处理单元150,湿法处理单元150根据预设规则开启以用于吸收排出气体中携带的逃逸的二氧化硫、三氧化硫、硫酸盐、氨和铵盐等,这延长了低温催化脱硝工序中的催化剂的寿命,保证了脱硝效率,降低了氨逃逸。并且,湿法处理单元150还将通过吸收得到的回收浆液作为脱硝还原剂回用至水泥生产的高温脱硝或低温脱硝工序,有效降低了脱硝还原剂的消耗从而降低脱硝成本。In the
在一些实施例中,回收浆液中包含的物质至少包括铵盐,且以氨基量计,铵盐的摩尔数量占回收浆液中包含的所有氨类物质的总摩尔数量的50%以上。换言之,所得到的回收浆液中所包含的物质以铵盐为主,浆液更稳定,不易形成二次氨逃逸。相比之下,现有技术中直接吸收氨气的方案中,形成的氨水比较不稳定,容易形成二次氨逃逸。In some embodiments, the substance contained in the recovered slurry includes at least ammonium salt, and the molar amount of the ammonium salt accounts for more than 50% of the total molar amount of all ammonia substances contained in the recovered slurry based on the amount of amino groups. In other words, the substances contained in the obtained recovered slurry are mainly ammonium salts, the slurry is more stable, and it is not easy to form secondary ammonia escape. In contrast, in the solution of directly absorbing ammonia gas in the prior art, the formed ammonia water is relatively unstable, and it is easy to form secondary ammonia escape.
在一些进一步的实施例中,为了尽量将氨转化为铵盐,湿法处理单元150中所用的吸收液可以包括稀硫酸、稀亚硫酸等。铵盐具体可以包括硫酸铵、硫酸氢铵、亚硫酸铵和亚硫酸氢铵的至少之一种,具体取决于所用的吸收液成分。In some further embodiments, in order to convert ammonia into ammonium salts as much as possible, the absorption liquid used in the
在一些实施例中,在每个生产周期中,生料磨120的运行状态包括开启状态和关闭状态。当生料磨120的运行状态为开启状态时,与排出气体进行热交换,当生料磨120的运行状态为关闭状态时,不与排出气体进行热交换。In some embodiments, in each production cycle, the operating state of the
一般情况下,当生料磨120处于开启状态时,由于该排出气体与生料进行了热交换,其到达低温脱硝单元140时温度较低,低温脱硝催化剂的脱硝效率会比较低,而当生料磨120处于关闭状态时,由于该排出气体不必与生料进行热交换,其温度较高,则低温脱硝催化剂的脱硝效率会较高,从而会影响整个系统的脱硝情况。In general, when the
考虑到上述情况,可相应地设置针对湿法处理单元150的预设规则,以实现期望的效果。Considering the above situation, preset rules for the
在一些实施例中,预设规则包括无论生料磨120的运行状态是否为开启状态湿法处理单元150均开启,也就是说,无论生料磨120处于开启状态还是处于关闭状态,湿法处理单元150均保持开启。相应地,湿法处理单元150还配置为无论生料磨120的运行状态是否为开启状态均保持开启并对经过选择性催化还原脱硝处理后的排出气体进行湿法吸收得到回收浆液。这种方式可以在适当增加系统的运行成本的基础上最大程度地保证逃逸氨的吸收。In some embodiments, the preset rule includes that the
在另一些实施例中,预设规则包括当生料磨120的运行状态是开启状态时,湿法处理单元150关闭,当生料磨120的运行状态是关闭状态时,湿法处理单元150开启。相应地,湿法处理单元150还配置为:当生料磨120的运行状态是开启状态时,湿法处理单元150关闭以不对排出气体进行湿法吸收;当生料磨120的运行状态是关闭状态时,湿法处理单元150开启,并对排出气体进行湿法吸收得到回收浆液。这种方式可以选择性开启湿法处理单元150,通过合理设置每个生产周期中生料磨120和湿法处理单元150的开启时间,就能够在保证脱硝效果的前提下,降低整个系统的运行成本。In other embodiments, the preset rules include that when the operating state of the
进一步地,低温脱硝单元140还被配置为当生料磨120的运行状态是开启状态时,低温脱硝单元140中的脱硝催化剂在选择性催化还原脱硝处理中吸附并存储排出气体中携带的氨,并且然后当生料磨的运行状态是关闭状态时,允许存储于脱硝催化剂内的氨与氮氧化物发生反应。Further, the low temperature denitration unit 140 is also configured to adsorb and store the ammonia carried in the exhaust gas by the denitration catalyst in the low temperature denitration unit 140 in the selective catalytic reduction denitrification process when the operating state of the
换言之,当生料磨120处于开启状态时,该排出气体的温度较低,低温脱硝催化剂的脱硝效率比较低。此时,通过水泥分解和高温脱硝单元110完成脱硝,剩余的氨逃逸后,在低温脱硝单元140中被低温脱硝催化剂吸附/吸收,得以大量储存。这样,湿法处理单元150不必启用,而是通过低温脱硝催化剂吸附/吸收即可控制氨逃逸。In other words, when the
当生料磨120处于关闭状态(即停磨)时,该排出气体的温度较高,低温脱硝催化剂的脱硝效果较高,此时,之前低温状态下储存于低温脱硝催化剂内的氨得以在催化剂内反应。具体地,催化剂一方面提供氧化性环境将二氧化硫氧化为亚硫酸根或硫酸根,另一方面提供反应平台,从而使得部分二氧化硫与氨反应生成铵盐。后置的湿法处理单元150开启,可以将逃逸的铵盐、氨、二氧化硫等吸收并回用至水泥分解和高温脱硝单元110。When the
在这种方式中,开生料磨120时被吸收的氨储存于低温脱硝催化剂中,等待停磨时再进行脱硝反应,所以不会浪费。另外,在停磨状态下,通常水泥窑系统(如分解炉)的排气中的硫(如二氧化硫、三氧化硫等)会超标,需要通过增加喷氨量来实现脱硫,导致氨耗量很大。通过加装低温脱硝单元140后,低温脱硝催化剂可以有效地使得氨与硫反应生成铵盐被排气带出,从而可以减少喷氨量。而且,由于生成了铵盐,后面的湿法处理单元150将其捕捉后,还可以形成较为稳定的回收浆液。In this way, the ammonia absorbed when the
在一些实施例中,在每个生产周期中,生料磨120处于开启状态的时间占比可大于或等于70%且小于100%,例如,可以为75%、80%、85%、90%、95%等。优选地,在每个生产周期中,生料磨120处于开启状态的时间占比可以为80%。通过合理设置生料磨120在每个生产周期中处于开启状态的时间占比,以尽量保证较好的水泥生产系统100的整个运行效率,包括余热利用效率、脱硝效率和还原剂回用效率等。In some embodiments, in each production cycle, the proportion of time that the
基于同一技术构思,本发明还提供了一种水泥生产系统100的气体处理方法。该水泥生产系统100的结构可如图1所示。图2示出了根据本发明一实施例的水泥生产系统100的气体处理方法的流程示意图。参见图2所示,该水泥生产系统100的气体处理方法至少可以包括以下步骤S202至步骤S204。Based on the same technical concept, the present invention also provides a gas treatment method for the
步骤S202,在每个生产周期中,根据生料磨120的运行状态,使水泥分解和高温脱硝单元110的排出气体依次经过或不经过生料磨120进行热交换、经过除尘单元130进行除尘和经过低温脱硝单元140进行选择性催化还原脱硝处理后,根据预设规则使处理后的排出气体经过湿法处理单元150进行湿法吸收得到回收浆液。Step S202, in each production cycle, according to the operating state of the
步骤S204,将回收浆液作为脱硝还原剂回用至水泥分解和高温脱硝单元110或低温脱硝单元140。Step S204, the recovered slurry is reused as a denitration reducing agent to the cement decomposition and high temperature denitration unit 110 or the low temperature denitration unit 140.
由于回收浆液中富含氨类还原性物质,在一些实施方案中,可以将回收浆液直接喷入水泥分解和高温脱硝单元110(如分解炉及其附近工段),实现SNCR脱硝。在另一些可替换的实施方案中,也可以先在回收浆液中加入碱性物质(如碳酸氢钠等),使其与铵盐反应生成氨气,再将氨气喷入水泥分解和高温脱硝单元110,实现SNCR脱硝。回收浆液回用至低温脱硝单元140时,方式与水泥分解和高温脱硝单元110类似,不再赘述。Since the recovered slurry is rich in ammonia-based reducing substances, in some embodiments, the recovered slurry can be directly sprayed into the cement decomposition and high-temperature denitration unit 110 (eg, a decomposition furnace and its adjacent sections) to achieve SNCR denitration. In other alternative embodiments, alkaline substances (such as sodium bicarbonate, etc.) can also be added to the recovered slurry to react with ammonium salts to generate ammonia gas, and then the ammonia gas is sprayed into the cement for decomposition and high-temperature denitration. Unit 110, realizes SNCR denitration. When the recovered slurry is reused to the low temperature denitration unit 140, the method is similar to that of the cement decomposition and high temperature denitration unit 110, and will not be repeated here.
在一些实施例中,生料磨120的运行状态包括开启状态和关闭状态;并且,在每个生产周期中,当生料磨120的运行状态为开启状态时,使水泥分解和高温脱硝单元110的排出气体经过生料磨120进行热交换,当生料磨120的运行状态为关闭状态时,使水泥分解和高温脱硝单元110的排出气体不经过生料磨120进行热交换。In some embodiments, the operating state of the
在一些实施例中,预设规则包括无论生料磨120的运行状态是否为开启状态均开启湿法处理单元150。相应地,根据预设规则使处理后的排出气体经过湿法处理单元150进行湿法吸收得到回收浆液的步骤包括:无论生料磨120的运行状态是否为开启状态均使处理后的排出气体经过湿法处理单元150进行湿法吸收得到回收浆液。In some embodiments, the preset rule includes turning on the
在另一些实施例中,预设规则包括当生料磨120的运行状态是开启状态时,关闭湿法处理单元150,当生料磨120的运行状态是关闭状态时,开启湿法处理单元150。相应地,根据预设规则使处理后的排出气体经过湿法处理单元150进行湿法吸收得到回收浆液的步骤包括:当生料磨120的运行状态是开启状态时,关闭湿法处理单元150,使处理后的排出气体不经过湿法处理单元150;当生料磨120的运行状态是关闭状态时,开启湿法处理单元150,并使处理后的排出气体经过湿法处理单元150进行湿法吸收得到回收浆液。In other embodiments, the preset rules include that when the operating state of the
在一些进一步的实施例中,还将低温脱硝单元140配置为使得当生料磨120的运行状态是开启状态时,低温脱硝单元140中的脱硝催化剂在选择性催化还原脱硝处理中吸附并存储排出气体中携带的氨,并且然后当生料磨的运行状态是关闭状态时,允许存储于脱硝催化剂内的氨与氮氧化物发生反应。In some further embodiments, the low temperature denitration unit 140 is also configured such that when the operating state of the
在一些实施例中,在每个生产周期中,生料磨120处于开启状态的时间占比大于或等于70%且小于100%。In some embodiments, the
优选地,在每个生产周期中,生料磨120处于开启状态的时间占比为80%。Preferably, in each production cycle, the
在一些实施例中,回收浆液中包含的物质至少包括铵盐,且以氨基量计,铵盐的摩尔数量占回收浆液中包含的所有氨类物质的总摩尔数量的50%以上。换言之,所得到的回收浆液中所包含的物质以铵盐为主。In some embodiments, the substance contained in the recovered slurry includes at least ammonium salt, and the molar amount of the ammonium salt accounts for more than 50% of the total molar amount of all ammonia substances contained in the recovered slurry based on the amount of amino groups. In other words, the substances contained in the obtained recovered slurry were mainly ammonium salts.
在一些进一步的实施例中,为了尽量将氨转化为铵盐,湿法处理单元150中所用的吸收液可以包括、稀亚硫酸等。铵盐具体可以包括硫酸铵、硫酸氢铵、亚硫酸铵和亚硫酸氢铵的至少之一种,具体取决于所用的吸收液成分。In some further embodiments, in order to convert ammonia into ammonium salts as much as possible, the absorption liquid used in the
上文中介绍了本发明的水泥生产系统100的气体处理方法的各环节的多种实施方式,下面将通过一个具体实施例来更详细地说明本发明的水泥生产系统100的气体处理方法的具体实现方式。Various embodiments of each link of the gas treatment method of the
图3示出了根据本发明另一实施例的水泥生产系统100的气体处理方法的流程示意图。本实施例中,在每个生产周期中,生料磨120处于开启状态的时间占比为80%。参见图3所示,该水泥生产系统100的气体处理方法包括以下步骤S302至步骤S316。FIG. 3 shows a schematic flowchart of a gas treatment method of the
步骤S302,确定生料磨120的运行状态为开启状态还是关闭状态。In step S302, it is determined whether the running state of the
步骤S304,若生料磨120的运行状态为开启状态,使水泥分解和高温脱硝单元110的排出气体经过生料磨120进行热交换。之后,执行步骤S308至S310。Step S304 , if the running state of the
步骤S306,若生料磨120的运行状态为关闭状态,使水泥分解和高温脱硝单元110的排出气体不经过生料磨120进行热交换。之后,执行步骤S312至S316。Step S306 , if the running state of the
步骤S308,使该排出气体经过除尘单元130进行除尘。In step S308, the exhaust gas is dedusted through the
步骤S310,使除尘后的排出气体经过低温脱硝单元140进行选择性催化还原脱硝处理。In step S310, the exhaust gas after dedusting is passed through the low-temperature denitration unit 140 for selective catalytic reduction and denitration treatment.
具体地,当生料磨120的运行状态是开启状态时,低温脱硝单元140中的脱硝催化剂在选择性催化还原脱硝处理中吸附/吸收排出气体中携带的氨,以将氨存储在低温脱硝催化剂内。Specifically, when the operating state of the
并且,此时湿法处理单元150关闭,选择性催化还原脱硝处理后的排出气体不经过湿法处理单元150。In addition, at this time, the
步骤S312,使该排出气体经过除尘单元130进行除尘。In step S312, the exhaust gas is dedusted through the
步骤S314,使除尘后的排出气体经过低温脱硝单元140进行选择性催化还原脱硝处理。In step S314, the exhaust gas after dedusting is passed through the low-temperature denitration unit 140 for selective catalytic reduction and denitration treatment.
具体地,当生料磨120处于关闭状态时,之前低温状态下储存于低温脱硝催化剂内的氨得以在催化剂内反应。催化剂一方面提供氧化性环境将二氧化硫氧化为亚硫酸根或硫酸根,另一方面提供反应平台,从而使得部分二氧化硫与氨反应生成铵盐。Specifically, when the
步骤S316,开启湿法处理单元150,并使处理后的排出气体经过湿法处理单元150进行湿法吸收得到回收浆液。In step S316, the
具体地,湿法处理单元150中所用的吸收液包括稀硫酸。以氨基量计,回收浆液中铵盐的摩尔数量占回收浆液中包含的所有氨类物质的总摩尔数量的50%以上。铵盐包括硫酸铵和/或硫酸氢铵。Specifically, the absorbing liquid used in the
在本实施例中,在水泥生产系统100运行过程中,将步骤S316中得到的回收浆液返回至水泥分解和高温脱硝单元110用作SNCR脱硝的还原剂。In this embodiment, during the operation of the
在此处所提供的说明书中,说明了大量具体细节。然而,能够理解,本发明的实施例可以在没有这些具体细节的情况下实践。在一些实例中,并未详细示出公知的方法、结构和技术,以便不模糊对本说明书的理解。In the description provided herein, numerous specific details are set forth. It will be understood, however, that embodiments of the invention may be practiced without these specific details. In some instances, well-known methods, structures and techniques have not been shown in detail in order not to obscure an understanding of this description.
至此,本领域技术人员应认识到,虽然本文已详尽示出和描述了本发明的多个示例性实施例,但是,在不脱离本发明精神和范围的情况下,仍可根据本发明公开的内容直接确定或推导出符合本发明原理的许多其他变型或修改。因此,本发明的范围应被理解和认定为覆盖了所有这些其他变型或修改。By now, those skilled in the art will recognize that, although various exemplary embodiments of the present invention have been illustrated and described in detail herein, the present invention may still be implemented in accordance with the present disclosure without departing from the spirit and scope of the present invention. The content directly determines or derives many other variations or modifications consistent with the principles of the invention. Accordingly, the scope of the present invention should be understood and deemed to cover all such other variations or modifications.
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Citations (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20040136890A1 (en) * | 2001-05-19 | 2004-07-15 | Jurgen Lang | Method for carrying out the selectively catalytic reduction of nitrogen oxides with ammonia in the lean exhaust gas of a combustion process |
| US20180050303A1 (en) * | 2015-04-24 | 2018-02-22 | Heidelbergcement Ag | Treatment of exhaust gases from cement clinker production |
| JP2018138771A (en) * | 2017-02-24 | 2018-09-06 | 三菱日立パワーシステムズ株式会社 | Denitration control device for gas turbine, gas turbine combined-cycle power generation facility, denitration control method for gas turbine and denitration control program for gas turbine |
| CN210613257U (en) * | 2019-08-29 | 2020-05-26 | 福建远致环保科技有限公司 | Cement industry flue gas dust removal denitration integration treatment system |
| CN210752027U (en) * | 2019-06-06 | 2020-06-16 | 天津水泥工业设计研究院有限公司 | Desulfurization, denitrification and dedusting ultralow emission system for producing cement by using low-sulfur raw materials |
| US20200248605A1 (en) * | 2019-01-31 | 2020-08-06 | Hyundai Motor Company | After treatment system and after treatment method for lean-burn engine |
| WO2020192114A1 (en) * | 2019-03-25 | 2020-10-01 | 中国科学院过程工程研究所 | Industrial flue-gas storage reduction and denitration system and method |
| CN112058058A (en) * | 2020-09-02 | 2020-12-11 | 北京金隅琉水环保科技有限公司 | Recovery and circulation system for escaped ammonia in cement kiln ammonia process denitration tail gas and control method thereof |
| CN112717692A (en) * | 2020-12-17 | 2021-04-30 | 浙江德创环保科技股份有限公司 | Flue gas denitration process for asphalt mixing plant |
| CN113332839A (en) * | 2021-04-25 | 2021-09-03 | 北京建筑材料科学研究总院有限公司 | Cement kiln flue gas desulfurization and denitrification coupling recycling system and method |
-
2022
- 2022-05-10 CN CN202210507175.6A patent/CN114904381B/en active Active
Patent Citations (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20040136890A1 (en) * | 2001-05-19 | 2004-07-15 | Jurgen Lang | Method for carrying out the selectively catalytic reduction of nitrogen oxides with ammonia in the lean exhaust gas of a combustion process |
| US20180050303A1 (en) * | 2015-04-24 | 2018-02-22 | Heidelbergcement Ag | Treatment of exhaust gases from cement clinker production |
| JP2018138771A (en) * | 2017-02-24 | 2018-09-06 | 三菱日立パワーシステムズ株式会社 | Denitration control device for gas turbine, gas turbine combined-cycle power generation facility, denitration control method for gas turbine and denitration control program for gas turbine |
| US20200248605A1 (en) * | 2019-01-31 | 2020-08-06 | Hyundai Motor Company | After treatment system and after treatment method for lean-burn engine |
| WO2020192114A1 (en) * | 2019-03-25 | 2020-10-01 | 中国科学院过程工程研究所 | Industrial flue-gas storage reduction and denitration system and method |
| CN210752027U (en) * | 2019-06-06 | 2020-06-16 | 天津水泥工业设计研究院有限公司 | Desulfurization, denitrification and dedusting ultralow emission system for producing cement by using low-sulfur raw materials |
| CN210613257U (en) * | 2019-08-29 | 2020-05-26 | 福建远致环保科技有限公司 | Cement industry flue gas dust removal denitration integration treatment system |
| CN112058058A (en) * | 2020-09-02 | 2020-12-11 | 北京金隅琉水环保科技有限公司 | Recovery and circulation system for escaped ammonia in cement kiln ammonia process denitration tail gas and control method thereof |
| CN112717692A (en) * | 2020-12-17 | 2021-04-30 | 浙江德创环保科技股份有限公司 | Flue gas denitration process for asphalt mixing plant |
| CN113332839A (en) * | 2021-04-25 | 2021-09-03 | 北京建筑材料科学研究总院有限公司 | Cement kiln flue gas desulfurization and denitrification coupling recycling system and method |
Non-Patent Citations (2)
| Title |
|---|
| 吕鹏 等: "《水泥窑饱和蒸汽低氨燃烧脱硝技术改造》", 中国水泥 * |
| 王昊: "《影响火电厂烟气脱硝效率的主要因素研究》", 内燃机与配件 * |
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|---|---|
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