CN215233230U - Device for producing ammonium sulfite and by-producing ammonium thiosulfate mixed nutrient solution - Google Patents
Device for producing ammonium sulfite and by-producing ammonium thiosulfate mixed nutrient solution Download PDFInfo
- Publication number
- CN215233230U CN215233230U CN202120683236.5U CN202120683236U CN215233230U CN 215233230 U CN215233230 U CN 215233230U CN 202120683236 U CN202120683236 U CN 202120683236U CN 215233230 U CN215233230 U CN 215233230U
- Authority
- CN
- China
- Prior art keywords
- absorption tower
- tower
- pipeline
- nutrient solution
- sulfur
- 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
Images
Abstract
The utility model discloses a device for producing ammonium sulfite and by-producing ammonium thiosulfate mixed nutrient solution, which can burn solid matters rich in sulfur, the generated flue gas enters a cyclone separation tower for dust removal, and the flue gas after dust removal enters a heat exchanger for cooling; then the flue gas enters a washing and purifying tower for washing; flue gas respectively enters a primary absorption tower, a secondary absorption tower and a tertiary absorption tower for absorption, high-concentration ammonium bisulfite solution generated by reaction is taken out from a bottom groove of the primary absorption tower and then neutralized in a neutralization tank, and solid ammonium sulfite is separated by a centrifugal machine in the neutralization tank through cooling crystallization; residual liquid in the neutralization tank enters a mixed nutrient solution generation kettle to perform a thionation reaction to generate ammonium thiosulfate mixed nutrient solution; the flue gas enters a water washing tower to be washed and then is discharged. The utility model discloses the device can obtain high-purity solid ammonium sulfite and byproduct ammonium thiosulfate mixed nutrient solution, has good special industrial use and prospect.
Description
Technical Field
The utility model relates to a mixed nutrient solution apparatus for producing, concretely relates to device of production ammonium sulfite and ammonium thiosulfate mixed nutrient solution.
Background
Sodium thiosulfate, also known as sodium bicarbonate and seawave are monoclinic white crystalline powder, are easily soluble in water and insoluble in alcohol, and are mainly used as reducing agents in the manufacturing of tetraethyl lead, dye intermediates and the like, electroplating industries of ore silver extraction and the like, and water purifying agents in water purification engineering. Dechlorinating agents for bleaching cotton fabrics in textile industry, sulfur dyes for dyeing wool fabrics, anti-whitening agents for indigo dyes, pulp dechlorinating agents, detergents, disinfectants and color fading agents in pharmaceutical industry, analytical reagents for chromatography, cobalt determination by drop analysis, photographic fixing agents, common reagents for dechlorinating agent volumetric analysis, blood sodium determination, preparation of injections and met-al medium, mordant, sodium thiosulfate are used as antidotes for cyanide.
The patent with publication number CN103788960A discloses a functional fertilizer and a repairing agent for repairing soil heavy metals, wherein modified attapulgite, chitosan, biochar and sodium thiosulfate are compounded, so that on one hand, the adsorption performance of the attapulgite and the biochar and the chelation effect of the chitosan are utilized to fix heavy metal ions in soil and prevent the heavy metal ions from being leached and migrated by runoff; on one hand, sodium thiosulfate is used for reducing high-valence heavy metal ions (such as hexavalent chromium ions) into low-valence states (such as trivalent chromium ions), so that the toxicity and the solubility of the heavy metal ions are reduced. The thiosulfate can also be used as an additive of a fertilizer, can be used together with a conventional chemical fertilizer and a compound fertilizer, and has better fertilizer efficiency.
Patent publication No. CN106809807A discloses a method for preparing sodium thiosulfate, which comprises preparing a mixed solution of sodium sulfite and sodium hydroxide, heating the sodium thiosulfate solution, stirring, filtering while hot, heating in a steam bath for evaporation, cooling, filtering under reduced pressure, and crystallizing. The method comprises the steps of reacting a sodium hydroxide solution with the molar concentration of 1mol/L with sulfur dioxide gas to generate a mixed solution, heating and mixing the reacted mixed solution with sulfur powder under the conditions that the pH =11 and the temperature is 101 ℃, adding activated carbon powder after 27min, stirring, filtering while hot, heating and evaporating in nitrogen airflow, cooling, crystallizing and drying.
The patent with publication number CN101891159A discloses a preparation method of analytically pure sodium thiosulfate, which comprises the steps of (1) placing distilled water and sodium sulfite into a stainless steel reactor, heating for dissolving, heating the solution to boiling after dissolving, slowly adding sulfur powder into the stainless steel reactor, boiling the reaction mixture for 2-3 hours until the solution is no longer alkaline, stopping heating, standing for 5-6 hours, and filtering to obtain a solution A; (2) heating and concentrating the solution A, concentrating the solution to 22-23 DEG Be, cooling to obtain crystals, transferring the crystals into a vacuum drier for drying at the temperature of 30-35 ℃, and taking out to obtain an analytically pure sodium thiosulfate finished product. The analytical pure sodium thiosulfate is synthesized by reacting sodium sulfite with sulfur powder, the process steps are simple, the operation is easy to control, the production efficiency is high, and the prepared sodium thiosulfate is low in impurity content, so that the product can be widely applied to the market.
Patent publication No. CN106430114A discloses a method for producing sodium thiosulfate pentahydrate, which is characterized by comprising the following steps: (1) adding water into the slag containing the elemental sulfur, and stirring, washing, filtering and separating to obtain a filter cake A and a filtrate A; (2) adding sodium sulfite and water into the filter cake A, wherein the addition of the sodium sulfite is 1.1-1.2 times of the theoretical value, and the addition of the water is 15-20 times of the slag material containing the elemental sulfur, and heating, stirring and leaching the mixed material; then filtering and washing are carried out to obtain a filter cake B containing noble metal and a filtrate B; and evaporating, cooling, crystallizing, overflowing, filtering, separating and drying the filtrate B to obtain the sodium thiosulfate pentahydrate. The invention effectively recovers valuable elements and obtains two products of sodium thiosulfate pentahydrate and sodium sulfate.
The patent with publication number CN104071759A discloses a novel preparation method of sodium thiosulfate, which relates to the technical field of chemical industry, and comprises the steps of selecting qualified soda ash, adding water, uniformly stirring and mixing, adding sulfur dioxide, reacting to obtain a sodium sulfite solution, putting into a high-pressure reaction kettle, continuously stirring, heating until the solution boils, adding sulfur, continuously stirring and heating for 1.5 hours to obtain a hot solution, and conveying into an oxidation reaction kettle to control the temperature in the kettle to be 70-80 ℃ for oxidation reaction. And (3) when the reactant turns yellow or white, inputting the solution into an evaporation kettle for evaporation, decoloring the activated carbon, performing filter pressing, cooling, crystallizing, centrifuging by using a centrifugal machine, screening out industrial-grade sodium thiosulfate, putting the industrial-grade sodium thiosulfate into the crystallization kettle again for recrystallization to obtain a sodium thiosulfate finished product, and packaging and warehousing the sodium thiosulfate finished product. The beneficial effects of the invention are: the preparation is convenient and simple, environment-friendly and pollution-free, the equipment investment is low, the purity is high, the operation is convenient, and the prepared sodium thiosulfate has a good using effect, and is safe and reliable.
In the prior art, the production process of thiosulfate comprises the steps of thionation, oxidation, evaporation, crystallization and the like, and is characterized in that a dilute sodium sulfide solution is concentrated to prepare a concentrated solution, the concentrated solution reacts with sulfur at a certain temperature to generate a sodium polysulfide solution, then air blowing is carried out to oxidize the sodium polysulfide solution to generate a dilute sodium bicarbonate solution, and a series of steps of evaporation, concentration, crystallization and the like are carried out to prepare a finished product. The existing thiosulfate preparation method has complex process, difficult control of the reaction process and serious pollution and waste. In addition, Chinese sulfur has high dependence on the outside, and the sulfur price is high. The Chinese sulfur yield, the imported quantity and the market data in 2019, the Chinese sulfur yield in 2019 is about 7440 kt, the year-by-year increase is 9.4%, the imported sulfur quantity is 11730 kt, the year-by-year increase is 8.8%, the Chinese imported Japan in 2019 has the Korean liquid sulfur quantity of 2039.9 kt, the Korean liquid sulfur quantity is basically equal to that in 2018, the Chinese sulfur market in 2019 is low all the way, the annual reduction amplitude is 50%, in the process, new records are repeatedly brushed on related data, the average value of sulfur in ports in China in 2019 reaches 1890 kt, the national sulfur yield in China in 2750 kt.2020 continues to be expected to increase, the imported quantity probably needs to see the overall performance of the port inventory consumption and the downstream, and comprehensively, the pressure borne by the sulfur market in 2020 is not less than the previous years. Due to the restriction of the factors, the currently produced thiosulfate fertilizer has high cost, the price is 6-10 times of that of the fertilizer represented by ammonium sulfate, and the application of the thiosulfate fertilizer in the aspect of agricultural fertilizers is limited due to the overhigh price.
The waste sulfur source treatment of high-energy-consumption enterprises in China is always the problem of headache of the enterprises. The waste sulfur sources mainly come from: black sulfur in a coking plant, secondary sulfur in a chemical fertilizer plant, sulfur filtration sulfur slag in a sulfuric acid plant, sulfur slag desulfurized by carbon disulfide, industrial defective sulfur, sulfur slag, sulfur mud, sulfur paste and the like. These substances themselves have a great environmental pollution and the emissions are restricted by national policies. Due to the low grade of the raw materials, if advanced equipment and processes are not provided, the investment for enterprises to use is very large, the income is very low, and if only special recycling items are provided on the waste resources, the risk is very large, and the investment is very high.
Ammonium sulfite is an important chemical product (the chemical industry standard of the people's republic of China, industrial ammonium sulfite, HG/T2784-1996), is a chemical fertilizer and a chemical agent, has larger and larger demand along with the popularization of the pulping process of the ammonium sulfite method, and plays a larger and larger role in the improvement of the traditional paper making industry.
Ammonium sulfite is one of the most common by-products of ammonia desulfurization technology. The ammonia desulfurization technology is to remove SO in flue gas by adopting ammonia as an absorbent2The process of (1). The ammonia desulphurization process has a plurality of characteristicsFirstly, ammonia is a good alkaline absorbent, the alkalinity is stronger than that of a calcium-based absorbent, and sulfur dioxide in ammonia absorption flue gas is a gas-gas reaction or a gas-liquid reaction, so that the reaction speed is high, the reaction is complete, the utilization rate of the absorbent is high, and the high desulfurization efficiency can be obtained. Compared with the calcium-based desulfurization process, the ammonia desulfurization system is simple, the equipment volume is small, no secondary pollution is caused, in addition, the desulfurization byproduct ammonium sulfate is a common chemical fertilizer, and the economic benefit can be greatly improved by the byproduct sales income.
When coal gangue, sulfur-containing minerals and the like are combusted, the discharged flue gas contains SO2. SO in flue gas2The content is usually low, typically between 300-. In the case of coal-fired boilers, the steam scale is from 1T/h to 2500T/h, the generator set capacity is from 6MW to 900MW, and the flue gas amount is from 1 ten thousand Nm3H to 250 ten thousand Nm3H, severe acid rain and SO have been generated2And (4) pollution. The ammonia desulphurization technology is to remove SO in the flue gas2The by-products are sulfuric acid, ammonium sulfate fertilizer and ammonium sulfite. The ammonia desulphurization technology can produce the commonly used solid ammonium sulfite, but because of SO in the flue gas2The content is generally lower and the quality of the produced product is lower.
In addition, the traditional desulfurization device adopting the ammonia desulfurization technology is a two-stage desulfurization tower, and the device is suitable for the gas which is self-smoke of factory tail gas and is not suitable for high-concentration sulfur dioxide gas generated by burning auxiliary sulfur substances. The concentration of sulfur dioxide gas generated by burning secondary sulfur species is high. For example, combustion of sulfur, if the combustion is sufficient, there is no residual O2SO in the combustion gas2The proportion of gas to the total volume of gas can reach 21%, excess air may be present in the actual combustion, and even SO, the SO produced2The volume ratio of the gas can reach 10 to 15 percent; if pyrite is burned, SO is produced2The volume ratio of the gas can reach 7 percent; the sulfur-rich active carbon (the sulfur dioxide content can reach about 70 percent generally) is formed in the desulfurization by the active carbon method, and SO is in gas generated after combustion2The content is also very high. High-concentration sulfur dioxide gas generated by burning secondary sulfur substances passes through the primary absorption tower and then remainsThe concentration of sulfur dioxide in the residual gas is still very high, the concentration of the discharged sulfur dioxide gas is difficult to reach the discharge requirement after the absorption of the secondary absorption tower, and if the concentration of ammonia in the secondary absorption tower is increased, the sulfur dioxide can be completely absorbed, but ammonia escape possibly exists, and resources are wasted.
In the standard of industrial ammonium sulfite in China (HG/T2784-1996), the requirements of qualified industrial-grade solid ammonium sulfite products are that the content of ammonium sulfite is not less than 85%, the content of ammonium bisulfite is not more than 1%, and the content of ammonium sulfate is not more than 7%. The common method for producing high-purity ammonium sulfite basically takes high-grade sulfide minerals as raw materials, adopts a single process to produce the ammonium sulfite, does not consider the problems of comprehensive utilization of resources and environmental protection because of the pure pursuit of optimization of products, has limited product quantity and high cost.
SUMMERY OF THE UTILITY MODEL
An object of the utility model is to provide a device of production ammonium sulfite and byproduct ammonium thiosulfate mixed nutrient solution to prior art's not enough.
The utility model adopts the technical proposal as follows.
The device for producing ammonium sulfite and by-producing ammonium thiosulfate mixed nutrient solution is characterized in that: the device comprises a sulfur incinerator, a cyclone separation tower, a heat exchanger, a washing and purifying tower, a primary absorption tower, a secondary absorption tower, a tertiary absorption tower, a tail gas absorption tower, a degassing tower, three circulating tanks, a washing circulating pool, a filter, an ammonium sulfite finished product packaging device, an ammonia water tank, a sulfur crushing tank, a steam generator, a centrifuge, a neutralization tank, an ammonium bicarbonate tank and a mixed nutrient solution generating kettle;
the sulfur burning furnace is connected with the cyclone separation tower through a pipeline; the cyclone separation tower is connected with the washing and purifying tower through a pipeline, and a heat exchanger is arranged on the pipeline; the bottom of the washing and purifying tower is connected with the degassing tower through a pipeline, and the top of the washing and purifying tower is connected with the bottom of the primary absorption tower through a pipeline; the bottom of the degassing tower is connected with a washing circulation pool through a pipeline; the washing circulation tank is connected with an atomizing spray head arranged at the top end in the washing purification tower through a pipeline, and a circulation pump is arranged on the pipeline; the top of the degassing tower is connected with the bottom of the primary absorption tower through a pipeline;
the first-stage absorption tower, the second-stage absorption tower and the third-stage absorption tower have the same structure and respectively comprise a tower body, the lower part of the tower body is provided with a gas inlet, the top of the tower body is provided with a gas outlet, a spray head and a plurality of purification chambers are sequentially arranged from top to bottom between the upper part of the gas inlet and the lower part of the gas outlet, and the bottom of the tower body is provided with a bottom groove; the bottom plate of the purifying chamber is provided with a plurality of holes for gas and absorption liquid to pass through; a circulating tank is respectively arranged below the first-stage absorption tower, the second-stage absorption tower and the third-stage absorption tower; the spray heads of the first-stage absorption tower, the second-stage absorption tower and the third-stage absorption tower are respectively connected with a circulating tank below the first-stage absorption tower, the second-stage absorption tower and the third-stage absorption tower through pipelines, and circulating pumps are arranged on the pipelines; the ammonia water tank is connected with each circulating tank through a pipeline; the gas outlet of the first-stage absorption tower is connected with the gas inlet of the second-stage absorption tower through a pipeline; the gas outlet of the second-stage absorption tower is connected with the gas inlet of the third-stage absorption tower through a pipeline; the gas outlet of the third-stage absorption tower is connected with the tail gas absorption tower;
the circulating tank below the third-stage absorption tower is connected with the circulating tank below the second-stage absorption tower through a pipeline; the circulating tank below the secondary absorption tower is connected with the circulating tank below the primary absorption tower through a pipeline;
the bottom groove of the primary absorption tower is connected with the neutralization tank through a pipeline; a centrifugal machine is arranged on the neutralization tank, and the ammonium sulfite finished product packaging device is connected with the centrifugal machine; the mixed nutrient solution generating kettle is connected with the neutralizing tank through a pipeline;
the ammonium bicarbonate groove is respectively connected with the mixed nutrient solution generating kettle and the neutralizing tank through pipelines;
the ammonia water tank is connected with the mixed nutrient solution generating kettle through a pipeline, and a valve is arranged on the pipeline;
the structure of the tail gas absorption tower is the same as that of the washing and purifying tower;
the mixed nutrient solution generating kettle is connected with a steam generator through a pipeline, and the steam generator is connected with a sulfur burner; the sulfur crushing tank is connected with the mixed nutrient solution generating kettle through a pipeline; the mixed nutrient solution generating kettle is connected with a gas inlet of the first-stage absorption tower, a gas inlet of the second-stage absorption tower or a gas inlet of the third-stage absorption tower through a pipeline; the filter is connected with the mixed nutrient solution generating kettle through a pipeline.
As a preferred technical scheme, a water cooling device is arranged on the heat exchanger.
As a preferred technical scheme, a water cooling device is arranged on the neutralization tank.
The temperature of the liquid in the neutralization tank is reduced to below 10 ℃ by a water cooling device.
According to the preferred technical scheme, a water tank is arranged below the tail gas absorption tower, a spraying device is arranged at the top end inside the tail gas absorption tower, and the bottom end of the tail gas absorption tower is connected with the water tank through a pipeline; the water tank is connected with the spraying device through a pipeline.
As a preferred technical scheme, the water tank is connected with a circulating tank below the third-stage absorption tower through a pipeline.
The process for producing ammonium sulfite and by-producing ammonium thiosulfate mixed nutrient solution is characterized by comprising the following steps:
burning sulfur in a sulfur burning furnace to produce smoke rich in high-concentration sulfur dioxide gas; enabling the flue gas to enter a cyclone separation tower for dust removal, enabling the flue gas after dust removal to enter a heat exchanger, and reducing the temperature to 60-70 ℃; the flue gas enters a washing and purifying tower, the structure of the washing and purifying tower is similar to that of a cyclone separation tower, only an atomizing nozzle is arranged at the upper part, and atomized water is sprayed by the atomizing nozzle to wash solid matters in the flue gas; then the flue gas enters a first-stage absorption tower, the first-stage absorption tower at least comprises a spray head, a plurality of purification chambers and a bottom groove from top to bottom, a circulating pump is arranged outside the tower, the solution in the bottom groove is continuously conveyed to the spray head through a pipeline, the bottom plate of each purification chamber is provided with a plurality of small holes, atomized solution is sprayed out of the spray head, and the solution is composed of ammonia water and (NH)4)2SO3The method comprises the following steps of controlling the pH value of a solution to be 5-6, enabling a high-concentration ammonium bisulfite solution generated by reaction to fall into a bottom tank of a primary absorption tower, and enabling the high-concentration ammonium bisulfite solution to flow into a neutralization tank from the bottom tank after the concentration meets the requirement; then the flue gas enters a secondary absorption tower; the second-stage absorption tower has the same structure as the first-stage absorption tower, and atomized solution is sprayed from the spray head and consists of ammonia water and (NH)4)2SO3The composition is characterized in that the pH value of the solution is controlled to be 6-7; then the flue gas enters a three-stage absorption tower; the third absorption tower has the same structure as the first absorption tower, and is sprayed with atomized solution comprising ammonia water and (NH)4)2SO3The composition is characterized in that the pH value of the solution is controlled to be 6-7; the flue gas discharged by the third-stage absorption tower is discharged by a tail gas absorption tower;
the structure of the tail gas absorption tower is the same as that of the washing and purifying tower;
measuring the concentration and volume of the bottom tank ammonium bisulfite solution of the first-stage absorption tower, and calculating the amount of ammonium bisulfite needed for neutralizing the ammonium bisulfite into a sulfurous acid solution; enabling the ammonium sulfite solution to flow into a neutralization tank, adding ammonium bicarbonate, cooling the neutralization tank by adopting a water cooling device, crystallizing saturated ammonium sulfite for a period of time, and depositing the saturated ammonium sulfite at the bottom of the neutralization tank; a centrifugal machine is arranged at the bottom of the neutralization tank, the crystallized solid ammonium sulfite is thrown out of the neutralization tank by the centrifugal machine, and a solid ammonium sulfite product is formed after collection;
the residual solution obtained after solid sulfurous acid is separated in the neutralization tank is introduced into a mixed nutrient solution generation kettle, the content of ammonium sulfite in the residual solution is measured, the number of ammonium and sulfur required for converting ammonium sulfite in the solution into ammonium thiosulfate is calculated, the number of required ammonium bicarbonate is converted according to the required number of ammonium and the concentration of low-concentration ammonia water, and the ammonium sulfite is converted into ammonia water, ammonium bicarbonate and excessive sulfur powder which are required by sodium thiosulfate and added into the mixed nutrient solution generation kettle;
a steam generator is adopted to cool the sulfur burning furnace, when the sulfur burning furnace burns, the temperature of the furnace body is kept at 750-800 ℃, water vapor generated by the steam generator is introduced into the mixed nutrient solution generating kettle, the temperature of liquid in the mixed nutrient solution generating kettle is slowly raised to 50-65 ℃ within 60-80 minutes, and gas generated by the mixed nutrient solution generating kettle is introduced into a primary absorption tower or a secondary absorption tower or a tertiary absorption tower;
continuously introducing the water vapor into the mixed nutrient solution generation kettle to ensure that the liquid temperature in the mixed nutrient solution generation kettle reaches 100-105 ℃, keeping the pressure of the mixed nutrient solution generation kettle at 0.05-0.1MPa, and preserving the heat for 2-4 hours, and introducing the gas in the mixed nutrient solution generation kettle into the primary absorption tower or the secondary absorption tower or the tertiary absorption tower when the pressure exceeds the pressure range; after the reaction is finished, introducing gas in the mixed nutrient solution generation kettle into a primary absorption tower, a secondary absorption tower or a tertiary absorption tower;
opening the mixed nutrient solution generating kettle, filtering to generate mixed nutrient solution, and putting the filtered residue into a combustion furnace for combustion to generate flue gas rich in high-concentration sulfur dioxide gas.
Before filtering to generate the mixed nutrient solution, the method also comprises the step of adding a nitrogen fertilizer and a phosphate fertilizer to adjust the fertilizer efficiency of the mixed nutrient solution.
The solution generated after washing the flue gas in the washing and purifying tower enters a degassing tower for degassing, the degassing tower is of an empty tower structure, and the top of the degassing tower is provided with a gas outlet; the solution after degassing enters a washing circulation tank for precipitation, and solid precipitates such as biochemical sulfur and the like which are rich in incomplete combustion are separated and then are put into a sulfur incinerator for combustion for cyclic utilization; the gas produced in the degassing tower is sent to the first-stage absorption tower.
And conveying the solution participating in the reaction in the third absorption tower to the second absorption tower for reaction, and conveying the solution participating in the reaction in the second absorption tower to the first absorption tower for reaction.
The sulfur is sulfur-containing substances generated after coal or petroleum desulfurization, and the sulfur content is not less than 85%.
The beneficial effects of the utility model are as follows.
1. The problem of tail gas emission is solved. The flue gas is dedusted by the cyclone separation tower, and the gas is cooled by the cooling equipment. If the secondary sulfur substances such as sulfur and the like are not fully combusted and possibly contain certain solid impurities such as biochemical sulfur and the like, the sulfur-rich gas is washed by water through the washing and purifying tower, and the impurities such as biochemical sulfur and the like which are not fully combusted can be washed out and recovered in the washing and circulating tank. The recovered biochemical sulfur-rich solid can be combusted again. The solution generated after the washing and purifying tower is washed contains certain SO2Further degassing may be carried out in a degassing column to recover SO therefrom2. SO with three absorption towers2In whichThe first-stage absorption tower is mainly used for treating high-concentration SO2Due to SO and concentration of ammonium bisulfite2The gas concentration is high, and the concentration of the ammonia water and the ammonium sulfite solution participating in the reaction is generally low (the concentration of pure ammonia water is 25% -33%), so that the purity of the generated ammonium bisulfite solution is high. Generally, in the first-stage absorption tower, the gas is continuously circulated, and the SO content in the gas is about 75 percent2Is absorbed. The second-stage absorption tower is mainly used for absorbing SO2And providing ammonium sulfite absorption liquid for the first-stage desulfurizing tower, wherein SO in the gas is2The concentration is obviously reduced, and the main component in the product is ammonium sulfite. Generally, in the secondary absorption tower, the gas is continuously circulated, and the SO content in the gas is about 75 percent2Is absorbed. The concentration of sulfur dioxide in the three-stage absorption tower is low, the concentration of ammonia in the absorption liquid is low, the residual ammonia in the reaction is little, the absorbed gas is washed by water, and SO in the gas2And the discharge amount of ammonia gas is very low, and the discharge requirement can be completely met. The desulfurizing tower is provided with a plurality of layers of purifying chambers, and solves the problems that in the prior art, gas is not fully contacted with circulating liquid, dead angles exist easily, and the desulfurizing efficiency is low.
2. The gas generated by the mixed nutrient solution generating kettle is recovered. The gas generated by the mixed nutrient solution generating kettle is mainly ammonia gas which is introduced into the first-stage absorption tower, the second-stage absorption tower or the third-stage absorption tower for continuous recycling, and the problem of large pollution in ammonium thiosulfate production in the prior art is solved.
3. Energy is saved. The mixed nutrient solution generating kettle is heated by water vapor, the energy generated by the water vapor comes from a sulfur incinerator, and meanwhile, excessive sulfur (1.02-1.05 times of the amount of the sulfur required by the reaction) is adopted, so that the energy generated by the sulfur incinerator is fully utilized, a good environment is created for the thionation reaction, and the thionation is full. The steam generator is adopted to cool the sulfur burning furnace, so that the temperature of the furnace body is kept at 750-800 ℃ when the sulfur burning furnace burns, the combustion gas of the sulfur burning furnace is ensured, and the generation of sublimed sulfur is reduced, thereby preventing the sublimed sulfur from being attached to a pipeline to block the pipeline during long-term operation, and reducing the content of impurities in the solution.
4. Solves the problem that the solid ammonium thiosulfate fertilizer easily causes harm to plants in the prior art, and has lower manufacturing cost. The solid thiosulfate fertilizer solution decomposes elemental sulfur, and is directly applied to leaves or roots of plants, so that the damage to the plants is easily caused, and the equation is as follows:
the utility model discloses, the mixed nutrient solution of ammonium thiosulfate is directly produced. The decomposition of the mixed nutrient solution containing thiosulfate is a long process, and the decomposed elemental sulfur has a good bactericidal effect. The liquid containing low-concentration thiosulfate is easy to treat, can avoid the harm to plants caused by solid thiosulfate fertilizer, and has little nitrogen component in soil dissolved out into rivers and lakes caused by nitrification.
The utility model discloses utilize ammonium bicarbonate to carry out the neutralization to the high concentration ammonium bisulfite solution that produces in the one-level absorption tower, impurity content is also very low in the ammonium sulfite crystal of being separated out after the cooling crystallization. The sulfur slag filtered by burning sulfur, the sulfur slag desulfurized by carbon disulfide, industrial defective sulfur, sulfur slag, sulfur mud, sulfur paste and the like can be used as raw materials of the sulfur burning furnace, for example, waste sulfur such as activated carbon rich in sulfur is formed in desulfurization by an activated carbon method, and the gas generated by burning is mainly SO2And CO2The ammonium hydrogen carbonate is generated by the reaction with ammonia water, which is needed by the method for neutralizing the ammonium hydrogen sulfite solution, so that industrial grade solid ammonium sulfite crystals with high purity can be produced by burning waste sulfur by using the method, and simultaneously ammonium thiosulfate is a byproduct. The solution remained after the ammonium bisulfite solution is neutralized by the method can be further supplemented into an absorption tower to be used as a desulfurizing agent. When the concentration of the dissolved liquid ammonia in the water washing tower is higher, the dissolved liquid ammonia can also be supplemented into the three-stage absorption tower. The utility model has the advantages of highly purifying SO2And other harmful acid gases, effectively improves the utilization rate of the ammonia absorbent, and the like, can obtain high-purity solid ammonium sulfite, and has good special industrial application and prospect.
Drawings
FIG. 1 is a schematic structural diagram of a preferred embodiment of the apparatus for producing mixed ammonium sulfite and ammonium thiosulfate nutrient solution of the present invention.
Fig. 2 is a partially enlarged view of a portion a of fig. 1.
Fig. 3 is a partially enlarged view of a portion B of fig. 1.
Fig. 4 is a partially enlarged view of a portion C of fig. 1.
FIG. 5 is a schematic structural diagram of a preferred embodiment of the apparatus for producing mixed ammonium sulfite and ammonium thiosulfate nutrient solution of the present invention.
Fig. 6 is a partially enlarged view of a portion D of fig. 5.
FIG. 7 is a schematic structural diagram of a preferred embodiment of the mixed nutrient solution producing ammonium sulfite and ammonium thiosulfate according to the present invention.
Fig. 8 is a partially enlarged view of a portion E of fig. 7.
A sulfur incinerator-1; a cyclone separation column-2; a heat exchanger-3; washing and purifying tower-4; a first-stage absorption tower-5; a secondary absorption tower-6; a third-stage absorption tower-7; a tail gas absorption tower-8; a degassing tower-9; a spray head-10; a clean room-11; a bottom plate-12; a bottom groove-13; a recycle tank-14; a washing circulation tank-15; a filter-16; an ammonium sulfite finished product packaging device-17; ammonia tank-18; a sulphur grinding tank-19; a steam generator-20; a centrifuge-21; neutralization tank-22; ammonium bicarbonate tank-23; mixing the nutrient solution to generate a kettle-24; circulating pump-25; a valve-26.
Detailed Description
Example 1. As shown in fig. 1-3, the process for producing ammonium sulfite and by-producing ammonium thiosulfate mixed nutrient solution is characterized by comprising the following steps:
putting sulfur into a sulfur incinerator 1 for combustion to generate flue gas rich in high-concentration sulfur dioxide gas; the flue gas enters a cyclone separation tower 2 for dust removal, the flue gas after dust removal enters a heat exchanger 3, and the temperature is reduced to 60-70 ℃; the flue gas enters a washing and purifying tower 4, the structure of the washing and purifying tower 4 is similar to that of the cyclone separation tower 2, only the upper part is provided with an atomizing nozzle 41, and atomized water sprayed by the atomizing nozzle 41 washes solid matters in the flue gas; followed byThe back flue gas gets into one-level absorption tower 5, and one-level absorption tower 5 is inside top-down including shower nozzle 10, several purge chamber 11 and kerve 13 at least, and the tower outside is equipped with the circulating pump, constantly carries the solution in kerve 13 in shower nozzle 10 through the pipeline, bottom plate 12 of purge chamber 11 has a plurality of apertures, by shower nozzle 10 blowout atomizing solution, this solution is by ammonia and (NH) solution4）2SO3The pH value of the solution is controlled to be 5-6, the high-concentration ammonium bisulfite solution generated by the reaction falls into a bottom groove 13 of a primary absorption tower 5, and flows into a neutralization tank 22 from the bottom groove 13 when the concentration meets the requirement; then the flue gas enters a secondary absorption tower 6; the second absorption tower 6 has the same structure as the first absorption tower 5, and the atomized solution is sprayed from the spray head 10, and the solution is composed of ammonia water and (NH)4）2SO3The composition is characterized in that the pH value of the solution is controlled to be 6-7; then the flue gas enters a three-stage absorption tower 7; the third absorption tower 7 has the same structure as the first absorption tower 5, and the atomized solution is sprayed from the spray head 10, and the solution is composed of ammonia water and (NH)4）2SO3The composition is characterized in that the pH value of the solution is controlled to be 6-7; and the flue gas discharged from the third-stage absorption tower 7 is discharged from a tail gas absorption tower 8. Cyclone separation towers, also known as cyclones, are a device used for the separation of gas-solid systems or liquid-solid systems. The working principle is that solid particles or liquid drops with larger inertial centrifugal force are thrown to the outer wall surface to be separated by the rotating motion caused by tangential introduction of air flow. The cyclone separator has the main characteristics of simple structure, high operation flexibility, high efficiency, convenient management and maintenance and low price, is used for collecting dust with the diameter of more than 5-10 mu m, is widely applied to the pharmaceutical industry, is particularly suitable for being used as an internal separation device of a fluidized bed reactor or a pre-separator under the conditions of coarse dust particles, high dust concentration and high temperature and high pressure, and is separation equipment with wide industrial application.
Measuring the concentration and volume of the ammonium bisulfite solution in the bottom tank 13 of the primary absorption tower 5, and calculating the amount of ammonium bicarbonate needed for neutralizing the ammonium bisulfite into the sulfurous acid solution; the ammonium sulfite solution flows into a neutralization tank 22, ammonium bicarbonate is added, a water cooling device is adopted to cool the neutralization tank 22, and saturated sulfurous acid is led to flow intoAmmonium salt is crystallized for a period of time and deposited into the bottom of neutralization tank 22; the bottom of the neutralization tank 22 is provided with a centrifuge 21, the crystallized solid ammonium sulfite is thrown out of the neutralization tank 22 by the centrifuge 21, and a solid ammonium sulfite product with a molecular formula of (NH) is formed after collection4）2SO3·H2O。
And (3) introducing the residual solution (the weight percentage of ammonium sulfite is about 20%) obtained after solid ammonium sulfite is separated in the neutralization tank 22 into a mixed nutrient solution generation kettle 24, measuring the ammonium sulfite content of the residual solution, calculating the ammonium quantity and the sulfur quantity required for converting ammonium sulfite in the solution into ammonium thiosulfate, converting the required ammonium bicarbonate quantity according to the required ammonium quantity and the concentration of low-concentration ammonia water, converting the ammonium sulfite into ammonia water, ammonium bicarbonate and excessive sulfur powder which are required for converting sodium thiosulfate and adding the ammonia water, the ammonium bicarbonate and the excessive sulfur powder into the mixed nutrient solution generation kettle 24. The excessive sulfur powder means that the adding amount of the sulfur powder is 1.01 to 1.05 times of the required amount of the reaction.
The steam generator 20 is adopted to cool the sulfur burner 1, so that when the sulfur burner 1 is burnt, the temperature of a furnace body is kept at 750 ℃, steam generated by the steam generator 20 is introduced into the mixed nutrient solution generation kettle 24, the temperature of liquid in the mixed nutrient solution generation kettle 24 is slowly raised to 50 ℃ within 60 minutes, and gas generated by the mixed nutrient solution generation kettle 24 is introduced into the primary absorption tower. The gas is mainly ammonia.
Continuously introducing the water vapor into the mixed nutrient solution generation kettle 24 to ensure that the liquid temperature in the mixed nutrient solution generation kettle 24 reaches 105 ℃, keeping the pressure of the mixed nutrient solution generation kettle 24 at 0.05MPa, preserving the heat for 2 hours, and introducing the gas in the mixed nutrient solution generation kettle 24 into the primary absorption tower 5 when the pressure exceeds the pressure range; and after the reaction is finished, introducing gas in the mixed nutrient solution generation kettle 24 into the primary absorption tower 5, wherein the gas is mainly ammonia gas.
The mixed nutrient solution generating kettle 24 is opened, the mixed nutrient solution is generated by filtration, and the filtered residue is put into a combustion furnace for combustion to generate flue gas rich in high-concentration sulfur dioxide gas.
Before filtering to generate the mixed nutrient solution, the method also comprises the step of adding a nitrogen fertilizer and a phosphate fertilizer to adjust the fertilizer efficiency of the mixed nutrient solution.
The solution generated after washing the flue gas in the washing and purifying tower 4 enters a degassing tower 9 for degassing, the degassing tower 9 is of an empty tower structure, and the top of the degassing tower is provided with a gas outlet; the solution after degassing enters a washing circulation pool 15 for precipitation, and solid precipitates such as biochemical sulfur and the like which are rich in incomplete combustion are separated and then are put into a sulfur incinerator 1 for combustion for recycling; the gas produced in the degassing tower 9 is sent to the primary absorption tower 5.
The solution in the third absorption tower 7 is sent to the second absorption tower 6 for reaction, and the solution in the second absorption tower 6 is sent to the first absorption tower 5 for reaction.
The sulfur is sulfur-containing substances generated after coal or petroleum desulfurization, and the sulfur content is not less than 85%.
The principle of ammonia desulfurization is to use ammonia water with a certain concentration and SO in flue gas2Reaction to desulfurize and produce NH42SO3The purpose of (1). The reaction equation is as follows:
S+O2→SO2 (1) ；
2NH3+SO2+H2O→（NH4）2SO3 (2)；
（NH4）2SO3+SO2+H2O→2NH4HSO3 (3)；
（NH4）HSO3+NH3→NH42SO3 (4)；
（NH4）2SO3 +2NH3H2O→（NH4）2SO3+2NH3+2H2O (5)；
（NH4）2SO3+S→（NH4）2S2SO3 (6)。
the device for producing the ammonium sulfite and by-producing the ammonium thiosulfate mixed nutrient solution by adopting the process is characterized in that: the device comprises a sulfur incinerator 1, a cyclone separation tower 2, a heat exchanger 3, a washing and purifying tower 4, a primary absorption tower 5, a secondary absorption tower 6, a tertiary absorption tower 7, a tail gas absorption tower 8, a degassing tower 9, three circulating tanks 14, a washing circulating pool 15, a filter 16, an ammonium sulfite finished product packaging device 17, an ammonia water tank 18, a sulfur crushing tank 19, a steam generator 20, a centrifuge 21, a neutralization tank 22, an ammonium bicarbonate tank 23 and a mixed nutrient solution generating kettle 24.
The sulfur incinerator 1 is connected with the cyclone separation tower 2 through a pipeline; the cyclone separation tower 2 is connected with a washing and purifying tower 4 through a pipeline, and a heat exchanger 3 is arranged on the pipeline; the bottom of the washing and purifying tower 4 is connected with the degassing tower 9 through a pipeline, and the top of the washing and purifying tower 4 is connected with the bottom of the primary absorption tower 5 through a pipeline; the bottom of the degassing tower 9 is connected with a washing circulation pool 15 through a pipeline; the washing circulation tank 15 is connected with an atomizing spray head 41 arranged at the top end in the washing and purifying tower 4 through a pipeline, and a circulation pump is arranged on the pipeline; the top of the degassing tower 9 is connected to the bottom of the primary absorption tower 5 through a pipeline. The sulfur burned by the sulfur incinerator 1 can be black sulfur of a coking plant, secondary sulfur of a chemical fertilizer plant, sulfur filtration sulfur slag of a sulfuric acid plant, sulfur slag desulfurized by carbon disulfide, industrial defective sulfur, sulfur slag, sulfur mud, sulfur paste and the like.
The primary absorption tower 5, the secondary absorption tower 6 and the tertiary absorption tower 7 have the same structure and respectively comprise a tower body, the lower part of the tower body is provided with a gas inlet, the top of the tower body is provided with a gas outlet, a spray head 10 and a plurality of purification chambers 11 are sequentially arranged from top to bottom between the upper part of the gas inlet and the lower part of the gas outlet, and the bottom of the tower body is provided with a bottom groove 13; a bottom plate 12 of the purifying chamber 11 is provided with a plurality of holes for allowing gas and absorption liquid to pass through; a circulating tank 14 is respectively arranged below the first-stage absorption tower 5, the second-stage absorption tower 6 and the third-stage absorption tower 7; the spray heads 10 of the first-stage absorption tower 5, the second-stage absorption tower 6 and the third-stage absorption tower 7 are respectively connected with a circulating tank 14 below the first-stage absorption tower, and a circulating pump is arranged on the pipeline; the ammonia tank 18 is connected with each circulation tank 14 through a pipeline; the gas outlet of the primary absorption tower 5 is connected with the gas inlet of the secondary absorption tower 6 through a pipeline; the gas outlet of the second-stage absorption tower 6 is connected with the gas inlet of the third-stage absorption tower 7 through a pipeline; and a gas outlet of the third-stage absorption tower 7 is connected with a tail gas absorption tower 8. The washing and purifying tower has the same structure as the tail gas absorption tower 8.
The circulating tank 14 below the third-stage absorption tower 7 is connected with the circulating tank 14 below the second-stage absorption tower 6 through a pipeline; the circulation tank 14 below the secondary absorption tower 6 is connected with the circulation tank 14 below the primary absorption tower 5 through a pipeline.
The bottom groove 13 of the primary absorption tower 5 is connected with a neutralization tank 22 through a pipeline; a centrifuge 21 is arranged on the neutralization tank 22, and the ammonium sulfite finished product packaging device 17 is connected with the centrifuge 21; the mixed nutrient solution generating kettle 24 is connected with the neutralization tank 22 through a pipeline; the ammonium bicarbonate groove 23 is respectively connected with the mixed nutrient solution generating kettle 24 and the neutralization tank 22 through pipelines.
The ammonia water tank 18 is connected with the mixed nutrient solution generating kettle 24 through a pipeline, and a valve is arranged on the pipeline.
The mixed nutrient solution generating kettle 24 is connected with the steam generator 20 through a pipeline, the steam generator 20 is connected with the sulfur burner, and energy is obtained from the sulfur burner 1; the sulfur crushing tank 19 is connected with the mixed nutrient solution generating kettle 24 through a pipeline; the mixed nutrient solution generating kettle 24 is connected with a gas inlet of the first-stage absorption tower 5, a gas inlet of the second-stage absorption tower 6 or a gas inlet of the third-stage absorption tower 7 through a pipeline; the filter 16 is connected to the mixed nutrient solution generating tank 24 through a pipe. The pH value of the mixed nutrient solution is controlled to be 8.6.
A water cooling device is arranged on the heat exchanger 3.
The neutralization tank 22 is provided with a water cooling device.
The temperature of the liquid in the neutralization tank is reduced to below 10 ℃ by a water cooling device.
A water tank 81 is arranged below the tail gas absorption tower 8, a spraying device 82 is arranged at the top end inside the tail gas absorption tower 8, and the bottom end of the tail gas absorption tower 8 is connected with the water tank 81 through a pipeline; the water tank 81 is connected with the spraying device 82 through a pipeline; the water tank 81 is connected to the circulation tank 14 below the tertiary absorption tower 7 through a pipe.
Brief introduction of the experiment: during the experiment, the flue gas is simulated flue gas consisting of mixed gas, the experimental process is the same as that in the figure 1, but the process is started from a first-stage absorption tower, and the simulated flue gas is preheated to 60 DEG CAnd then entering the flow. Test example 1. Simulating the smoke composition: 78% of N 23% of O 215% SO23% of CO2And water vapor. Flue gas flow rate: 1m3And/min. Circulating ammonia water and (NH) in the first-stage absorption tower4)2SO3The pH value of the solution is 5-6; circulating ammonia water and (NH) in secondary absorption tower4)2SO3The pH value of the solution is 6-7; circulating ammonia water and (NH) in three-stage absorption tower4)2SO3The pH value of the solution is 6-7. And (3) test results: flue gas flow rate of 1m3Min, SO after purification2Content 57 ppm, NH after purification3The content is 31 ppm, and the impurity content in solid ammonium sulfite is 5 percent. The produced mixed nutrient solution is colorless and transparent, and the impurity content is less than 0.5 percent.
Test example 2. Simulating the smoke composition: 78% of N 24% of O 210% SO27% of CO2And water vapor. Flue gas flow rate: 1m3And/min. Circulating ammonia water and (NH) in the first-stage absorption tower4)2SO3The pH value of the solution is 5-6; circulating ammonia water and (NH) in secondary absorption tower4)2SO3The pH value of the solution is 6-7; circulating ammonia water and (NH) in three-stage absorption tower4)2SO3The pH value of the solution is 6-7. And (3) test results: flue gas flow rate of 1m3Min, SO after purification2Content 65 ppm, NH after purification3The content is 28 ppm, and the impurity content in solid ammonium sulfite is 4 percent. The produced mixed nutrient solution is colorless and transparent, and the impurity content is less than 0.5 percent.
Test example 3: the simulated smoke composition is as follows: 78% of N 28% of O 27% SO25% of CO2And water vapor. Flue gas flow rate: 1m3And/min. Circulating ammonia water and (NH) in the first-stage absorption tower4)2SO3The pH value of the solution is 6-7; circulating ammonia water and (NH) in secondary absorption tower4)2SO3The pH value of the solution is 6-7; circulating ammonia water and (NH) in three-stage absorption tower4)2SO3The pH of the solution was 67. And (3) test results: flue gas flow rate of 1m3Min, SO after purification2Content 58ppm, NH after purification3The content is 62ppm, and the impurity content in solid ammonium sulfite is 5 percent. The produced mixed nutrient solution is colorless and transparent, and the impurity content is less than 0.5 percent.
Test example 4: the simulated smoke composition is as follows: 78% of N 23% of O2% of 10% SO28% of CO2And water vapor. Flue gas flow rate: 1m3And/min. Circulating ammonia water and (NH) in the first-stage absorption tower4)2SO3The pH value of the solution is 5-6; circulating ammonia water and (NH) in secondary absorption tower4)2SO3The pH value of the solution is 6-7; circulating ammonia water and (NH) in three-stage absorption tower4)2SO3The pH value of the solution is 6-7. And (3) test results: flue gas flow rate of 1m3Min, SO after purification2Content 62ppm, NH after purification3The content is 27 ppm, and the impurity content in solid ammonium sulfite is 5 percent. The produced mixed nutrient solution is colorless and transparent, and the impurity content is less than 0.5 percent.
Test example 5: 78% of N 23% of O2% of 12% SO2、6%CO2And water vapor. Flue gas flow rate: 1m3And/min. Circulating ammonia water and (NH) in the first-stage absorption tower4)2SO3The pH value of the solution is 5-6; circulating ammonia water and (NH) in secondary absorption tower4)2SO3The pH value of the solution is 6-7; circulating ammonia water and (NH) in three-stage absorption tower4)2SO3The pH value of the solution is 6-7. And (3) test results: flue gas flow rate of 1m3Min, SO after purification2Content 52ppm, NH after purification3The content is 25 ppm, and the impurity content in solid ammonium sulfite is 4 percent. The produced liquid fertilizer is colorless and transparent, and the impurity content is less than 0.5 percent.
The beneficial effects of the utility model are as follows.
1. The problem of tail gas emission is solved. The flue gas is dedusted by the cyclone separation tower 2, and the gas is cooled by cooling equipment. If the secondary sulfur substances such as sulfur are not sufficiently combusted, the secondary sulfur substances are mixed with the primary sulfur substancesThe sulfur-rich gas is washed by the washing and purifying tower 4, and impurities such as biochemical sulfur which are not fully combusted can be washed out and recovered in the washing and circulating tank 15. The recovered biochemical sulfur-rich solid can be combusted again. The solution generated after the washing and purifying tower is washed contains certain SO2Further degassing may be carried out in a degassing column 9 to recover SO therefrom2. SO with three absorption towers2Wherein the first-stage absorption tower is mainly used for treating high-concentration SO2Due to SO and concentration of ammonium bisulfite2The gas concentration is very high, and the concentration of the ammonia water and the ammonium sulfite solution which participate in the reaction is generally 25 to 33 percent of that of the lower pure ammonia water, so that the purity of the generated ammonium bisulfite solution is very high. Generally, in the first-stage absorption tower, the gas is continuously circulated, and the SO content in the gas is about 75 percent2Is absorbed. The second-stage absorption tower is mainly used for absorbing SO2And providing ammonium sulfite absorption liquid for the first-stage desulfurizing tower, wherein SO in the gas is2The concentration is obviously reduced, and the main component in the product is ammonium sulfite. Generally, in the secondary absorption tower, the gas is continuously circulated, and the SO content in the gas is about 75 percent2Is absorbed. The concentration of sulfur dioxide in the three-stage absorption tower is low, the concentration of ammonia in the absorption liquid is low, the residual ammonia in the reaction is little, the absorbed gas is washed by water, and SO in the gas2And the discharge amount of ammonia gas is very low, and the discharge requirement can be completely met. The desulfurizing tower is provided with a plurality of layers of purifying chambers, and solves the problems that in the prior art, gas is not fully contacted with circulating liquid, dead angles exist easily, and the desulfurizing efficiency is low.
2. The gas generated in the mixed nutrient solution generating tank 24 is recovered. The gas generated by the mixed nutrient solution generating kettle 24 is mainly ammonia gas which is introduced into the first-stage absorption tower 5, the second-stage absorption tower 6 or the third-stage absorption tower 7 for continuous recycling, and the problem of large pollution in the production of ammonium thiosulfate in the prior art is solved.
3. Energy is saved. The mixed nutrient solution generating kettle 24 is heated by water vapor, the energy generated by the water vapor comes from the sulfur incinerator 1, meanwhile, the excessive sulfur reaction is adopted, the amount of the sulfur is 1.02-1.05 times of the amount of the sulfur, the energy generated by the sulfur incinerator 1 is fully utilized, a good environment is created for the sulfur reaction, and the sulfur is fully reacted. The steam generator 20 is adopted to cool the sulfur incinerator 1, so that when the sulfur incinerator 1 burns, the furnace body temperature is kept at 750-800 ℃, the combustion gas of the sulfur incinerator 1 is ensured, the generation of sublimed sulfur is reduced, the sublimed sulfur is prevented from being attached to a pipeline to block the pipeline during long-term operation, and the content of impurities in the solution is also reduced.
4. Solves the problem that the solid ammonium thiosulfate fertilizer easily causes harm to plants in the prior art, and has lower manufacturing cost. The solid thiosulfate fertilizer solution decomposes elemental sulfur, and is directly applied to leaves or roots of plants, so that the damage to the plants is easily caused, and the equation is as follows:
the utility model discloses, the mixed nutrient solution of ammonium thiosulfate is directly produced. The decomposition of the mixed nutrient solution containing thiosulfate is a long process, and the decomposed elemental sulfur has a good bactericidal effect. The liquid containing low-concentration thiosulfate is easy to treat, can avoid the harm to plants caused by solid thiosulfate fertilizer, and has little nitrogen component in soil dissolved out into rivers and lakes caused by nitrification.
The utility model discloses utilize ammonium bicarbonate to carry out the neutralization to the high concentration ammonium bisulfite solution that produces in the one-level absorption tower, impurity content is also very low in the ammonium sulfite crystal of being separated out after the cooling crystallization. The sulfur slag filtered by burning sulfur, the sulfur slag desulfurized by carbon disulfide, industrial defective sulfur, sulfur slag, sulfur mud, sulfur paste and the like can be used as raw materials of the sulfur burning furnace 1, for example, waste sulfur such as activated carbon rich in sulfur is formed in the desulfurization by an activated carbon method, and the generated gas of combustion is mainly SO2And CO2The ammonium hydrogen carbonate is generated by the reaction with ammonia water, which is needed by the method for neutralizing the ammonium hydrogen sulfite solution, so industrial grade solid ammonium sulfite crystals with high purity can be produced by burning waste sulfur by using the method,simultaneously, the byproduct ammonium thiosulfate is produced. The solution remained after the ammonium bisulfite solution is neutralized by the method can be further supplemented into an absorption tower to be used as a desulfurizing agent. When the concentration of the dissolved liquid ammonia in the water washing tower is higher, the dissolved liquid ammonia can also be supplemented into the three-stage absorption tower. The utility model has the advantages of highly purifying SO2And other harmful acid gases, effectively improves the utilization rate of the ammonia absorbent, and the like, can obtain high-purity solid ammonium sulfite, and has good special industrial application and prospect.
Example 2. As shown in fig. 4 to 5, the present embodiment is different from embodiment 1 in that: the steam generator 20 is adopted to cool the sulfur burner 1, so that when the sulfur burner 1 is burnt, the temperature of a furnace body is kept at 800 ℃, steam generated by the steam generator 20 is introduced into the mixed nutrient solution generation kettle 24, the temperature of liquid in the mixed nutrient solution generation kettle 24 is slowly raised to 65 ℃ within 80 minutes, and gas generated by the mixed nutrient solution generation kettle 24 is introduced into the secondary absorption tower 6. The gas is mainly ammonia. Continuously introducing the water vapor into the mixed nutrient solution generation kettle 24 to ensure that the temperature of the liquid in the mixed nutrient solution generation kettle 24 is 100 ℃, keeping the pressure of the mixed nutrient solution generation kettle 24 at 0.1MPa, preserving the heat for 4 hours, and introducing the gas in the mixed nutrient solution generation kettle 24 into the secondary absorption tower 6 when the pressure exceeds the pressure range; after the end, the gas in the mixed nutrient solution generating kettle 24 is introduced into the secondary absorption tower 6. The pH value of the mixed nutrient solution is adjusted to be controlled at 8.5 by adding a potassium hydroxide solution.
Example 3. As shown in fig. 6 to 7, the present embodiment is different from embodiment 1 in that: the steam generator 20 is adopted to cool the sulfur incinerator 1, so that when the sulfur incinerator 1 burns, the temperature of the incinerator body is kept at 790 ℃, steam generated by the steam generator 20 is introduced into the mixed nutrient solution generation kettle 24, the temperature of liquid in the mixed nutrient solution generation kettle 24 is slowly raised to 60 ℃ within 70 minutes, and gas generated by the mixed nutrient solution generation kettle 24 is introduced into the three-stage absorption tower 7. The gas is mainly ammonia. Continuously introducing the water vapor into the mixed nutrient solution generation kettle 24 to ensure that the temperature of the liquid in the mixed nutrient solution generation kettle 24 is 102 ℃, keeping the pressure of the mixed nutrient solution generation kettle 24 at 0.06MPa and preserving the heat for 3 hours, and introducing the gas in the mixed nutrient solution generation kettle 24 into the three-stage absorption tower 7 when the pressure exceeds the pressure range; after the end, the gas in the mixed nutrient solution generating kettle 24 is introduced into the three-stage absorption tower 7. The pH value of the mixed nutrient solution is controlled to be 8.3 by adding a potassium hydroxide solution.
The above-mentioned embodiments are only for understanding the present invention, and are not intended to limit the technical solutions of the present invention, and those skilled in the relevant art can make various changes or modifications based on the technical solutions described in the claims, and all equivalent changes or modifications should be covered by the scope of the claims of the present invention. The parts of the present invention not described in detail are the known techniques of those skilled in the art.
Claims (5)
1. The utility model provides a device of production ammonium sulfite and byproduct ammonium thiosulfate mixed nutrient solution which characterized in that: the device comprises a sulfur incinerator, a cyclone separation tower, a heat exchanger, a washing and purifying tower, a primary absorption tower, a secondary absorption tower, a tertiary absorption tower, a tail gas absorption tower, a degassing tower, three circulating tanks, a washing circulating pool, a filter, an ammonium sulfite finished product packaging device, an ammonia water tank, a sulfur crushing tank, a steam generator, a centrifuge, a neutralization tank, an ammonium bicarbonate tank and a mixed nutrient solution generating kettle;
the sulfur burning furnace is connected with the cyclone separation tower through a pipeline; the cyclone separation tower is connected with the washing and purifying tower through a pipeline, and a heat exchanger is arranged on the pipeline; the bottom of the washing and purifying tower is connected with the degassing tower through a pipeline, and the top of the washing and purifying tower is connected with the bottom of the primary absorption tower through a pipeline; the bottom of the degassing tower is connected with a washing circulation pool through a pipeline; the washing circulation tank is connected with an atomizing spray head arranged at the top end in the washing purification tower through a pipeline, and a circulation pump is arranged on the pipeline; the top of the degassing tower is connected with the bottom of the primary absorption tower through a pipeline;
the first-stage absorption tower, the second-stage absorption tower and the third-stage absorption tower have the same structure and respectively comprise a tower body, the lower part of the tower body is provided with a gas inlet, the top of the tower body is provided with a gas outlet, a spray head and a plurality of purification chambers are sequentially arranged from top to bottom between the upper part of the gas inlet and the lower part of the gas outlet, and the bottom of the tower body is provided with a bottom groove; the bottom plate of the purifying chamber is provided with a plurality of holes for gas and absorption liquid to pass through; a circulating tank is respectively arranged below the first-stage absorption tower, the second-stage absorption tower and the third-stage absorption tower; the spray heads of the first-stage absorption tower, the second-stage absorption tower and the third-stage absorption tower are respectively connected with a circulating tank below the first-stage absorption tower, the second-stage absorption tower and the third-stage absorption tower through pipelines, and circulating pumps are arranged on the pipelines; the ammonia water tank is connected with each circulating tank through a pipeline; the gas outlet of the first-stage absorption tower is connected with the gas inlet of the second-stage absorption tower through a pipeline; the gas outlet of the second-stage absorption tower is connected with the gas inlet of the third-stage absorption tower through a pipeline; the gas outlet of the third-stage absorption tower is connected with the tail gas absorption tower;
the circulating tank below the third-stage absorption tower is connected with the circulating tank below the second-stage absorption tower through a pipeline; the circulating tank below the secondary absorption tower is connected with the circulating tank below the primary absorption tower through a pipeline;
the bottom groove of the primary absorption tower is connected with the neutralization tank through a pipeline; a centrifugal machine is arranged on the neutralization tank, and the ammonium sulfite finished product packaging device is connected with the centrifugal machine; the mixed nutrient solution generating kettle is connected with the neutralizing tank through a pipeline;
the ammonium bicarbonate groove is respectively connected with the mixed nutrient solution generating kettle and the neutralizing tank through pipelines;
the ammonia water tank is connected with the mixed nutrient solution generating kettle through a pipeline, and a valve is arranged on the pipeline;
the structure of the tail gas absorption tower is the same as that of the washing and purifying tower;
the mixed nutrient solution generating kettle is connected with a steam generator through a pipeline, and the steam generator is connected with a sulfur burner; the sulfur crushing tank is connected with the mixed nutrient solution generating kettle through a pipeline; the mixed nutrient solution generating kettle is connected with a gas inlet of the first-stage absorption tower, a gas inlet of the second-stage absorption tower or a gas inlet of the third-stage absorption tower through a pipeline; the filter is connected with the mixed nutrient solution generating kettle through a pipeline.
2. The apparatus for producing ammonium sulfite and co-producing mixed nutrient solution of ammonium thiosulfate as claimed in claim 1, characterized in that: the heat exchanger is provided with a water cooling device.
3. The apparatus for producing ammonium sulfite and co-producing mixed nutrient solution of ammonium thiosulfate as claimed in claim 1, characterized in that: a water cooling device is arranged on the neutralization tank.
4. The apparatus for producing ammonium sulfite and co-producing mixed nutrient solution of ammonium thiosulfate as claimed in claim 1, characterized in that: a water tank is arranged below the tail gas absorption tower, a spraying device is arranged at the top end inside the tail gas absorption tower, and the bottom end of the tail gas absorption tower is connected with the water tank through a pipeline; the water tank is connected with the spraying device through a pipeline.
5. The apparatus for producing ammonium sulfite and co-producing mixed nutrient solution of ammonium thiosulfate as claimed in claim 4, characterized in that: the water tank is connected with a circulating tank below the third-stage absorption tower through a pipeline.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202120683236.5U CN215233230U (en) | 2021-04-04 | 2021-04-04 | Device for producing ammonium sulfite and by-producing ammonium thiosulfate mixed nutrient solution |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202120683236.5U CN215233230U (en) | 2021-04-04 | 2021-04-04 | Device for producing ammonium sulfite and by-producing ammonium thiosulfate mixed nutrient solution |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN215233230U true CN215233230U (en) | 2021-12-21 |
Family
ID=79507411
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202120683236.5U Active CN215233230U (en) | 2021-04-04 | 2021-04-04 | Device for producing ammonium sulfite and by-producing ammonium thiosulfate mixed nutrient solution |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN215233230U (en) |
-
2021
- 2021-04-04 CN CN202120683236.5U patent/CN215233230U/en active Active
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CA2682402C (en) | Process and apparatus for carbon capture and elimination of multi-pollutants in flue gas from hydrocarbon fuel sources and recovery of multiple by-products | |
| CN106430116B (en) | A method of the sulphur-bearing waste solution extracting sulfuric acid generated using coal gas wet oxidation method | |
| CN105036438B (en) | A kind of sodium alkali desulfurization waste liquid method for innocent treatment | |
| CN111701419B (en) | Sodium-alkali dry-method desulfurized fly ash recycling method | |
| CN104923044B (en) | Smoke gas treatment system and method based on ozone | |
| CN205653162U (en) | System for sulphuric acid is prepared to sulphur waste liquid that contains that utilizes coal gas wet oxidation process to produce | |
| CN112973412A (en) | Process and device for producing ammonium sulfite and by-producing ammonium thiosulfate liquid fertilizer | |
| CN105600990A (en) | Method for recycling coke oven gas desulfurization and decyanation waste liquid to reclaim sulfur, ammonium sulfate and catalysts | |
| CN114620692A (en) | Process for preparing sulfuric acid by carrying out salt extraction and co-firing on coking desulfurization foam sulfur melting and desulfurization waste liquid melting method | |
| CN103288286A (en) | Catalytic oxidation treatment method for desulfurized waste liquid | |
| CN112973410A (en) | Process and device for producing ammonium sulfite and by-producing ammonium thiosulfate mixed nutrient solution | |
| CN104773742B (en) | A kind of process for purification of thick ammonium sulfate | |
| CN112973409A (en) | Process and device for producing ammonium sulfite and by-producing thiosulfate liquid fertilizer | |
| CN215233230U (en) | Device for producing ammonium sulfite and by-producing ammonium thiosulfate mixed nutrient solution | |
| CN104891464B (en) | The method of glyphosate waste material and yellow phosphoric tail gas coproduction Quadrafos | |
| CN215138504U (en) | Device for producing ammonium sulfite and by-producing thiosulfate mixed nutrient solution | |
| CN215138505U (en) | Device for producing ammonium sulfite and by-producing ammonium thiosulfate liquid fertilizer | |
| CN215276588U (en) | Device for producing ammonium sulfite and by-producing thiosulfate liquid fertilizer | |
| CN105727714B (en) | A kind of process and device for producing NaHS | |
| CN105731497B (en) | A kind of utilization sour gas produces the method and device of sodium acid carbonate | |
| CN1273389C (en) | Method of preparing manganese sulphate using gray manganese ore and dialozite to adsorb sulfur dioxide waste gas | |
| CN105642090B (en) | A kind of Acidic Gas Treating method and device | |
| CN101757843B (en) | Improved process for performing ammonium sulfite pulping by using sulfur-containing flue gas absorber | |
| CN112973411A (en) | Process and device for producing ammonium sulfite and byproduct thiosulfate mixed nutrient solution | |
| CN109110859A (en) | A kind of coking desulfurization waste liquor advanced treatment process |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| GR01 | Patent grant | ||
| GR01 | Patent grant |