WO2018223546A1 - System and method for desulfurizing coal and recovering elemental sulfur - Google Patents

System and method for desulfurizing coal and recovering elemental sulfur Download PDF

Info

Publication number
WO2018223546A1
WO2018223546A1 PCT/CN2017/100690 CN2017100690W WO2018223546A1 WO 2018223546 A1 WO2018223546 A1 WO 2018223546A1 CN 2017100690 W CN2017100690 W CN 2017100690W WO 2018223546 A1 WO2018223546 A1 WO 2018223546A1
Authority
WO
WIPO (PCT)
Prior art keywords
coal
unit
microwave
elemental sulfur
raw coal
Prior art date
Application number
PCT/CN2017/100690
Other languages
French (fr)
Chinese (zh)
Inventor
朱廷钰
郭旸旸
刘建民
薛建明
董月红
Original Assignee
中国科学院过程工程研究所
国电科学技术研究院
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by 中国科学院过程工程研究所, 国电科学技术研究院 filed Critical 中国科学院过程工程研究所
Publication of WO2018223546A1 publication Critical patent/WO2018223546A1/en

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B17/00Sulfur; Compounds thereof
    • C01B17/02Preparation of sulfur; Purification
    • C01B17/04Preparation of sulfur; Purification from gaseous sulfur compounds including gaseous sulfides
    • C01B17/0404Preparation of sulfur; Purification from gaseous sulfur compounds including gaseous sulfides by processes comprising a dry catalytic conversion of hydrogen sulfide-containing gases, e.g. the Claus process
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L9/00Treating solid fuels to improve their combustion
    • C10L9/02Treating solid fuels to improve their combustion by chemical means
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency

Definitions

  • the invention belongs to the technical field of coal cleaning, and relates to a system and a method for desulfurizing coal and recovering and producing elemental sulfur.
  • microwave desulfurization is a new method for desulfurization of high-sulfur coal in recent years.
  • the microwave is an electromagnetic wave with a frequency of 0.3-300 GHz and a wavelength of 1 mm-100 cm.
  • the inorganic sulfur such as pyrite in the coal is decomposed under microwave, mainly releasing H 2 S.
  • H 2 S and a small amount of SO 2 form elemental sulfur on the coal surface, and pyrite is converted into magnetic pyrite under the action of high temperature. This method can remove about 50% of sulfur in coal.
  • the present invention aims to provide a system and method for desulfurizing coal and recovering elemental sulfur, which can simultaneously remove and recover sulfur in coal to make total sulfur in coal.
  • the quantity control is below 2.0%, the total recovery rate of sulfur element is not less than 40%, safe and energy saving, suitable for desulfurization and sulfur recovery of various coal high-sulfur coal.
  • One of the objects of the present invention is to provide a system for desulfurizing coal and recovering elemental sulfur, including a microwave desulfurization unit, and further comprising:
  • Coal drying unit for containing SO 2 from flue gas for coal drying, the resulting dried coal and flue gas discharged after heat exchange;
  • An exhaust gas collecting unit for collecting the H 2 S-containing gas generated by the microwave desulfurization unit
  • An elemental sulfur reaction unit for reacting between the H 2 S-containing gas and the heat-exchanged coal-fired flue gas to produce elemental sulfur
  • the discharge port of the raw coal drying unit is connected to the feed port of the microwave desulfurization unit
  • the exhaust gas collection unit is disposed at the air outlet of the microwave desulfurization unit
  • the air inlet of the elemental sulfur reaction unit is respectively separated from the raw coal
  • the air outlet of the drying unit is connected to the air outlet of the exhaust gas collection unit.
  • the raw coal drying unit is dried by the waste heat of coal-fired flue gas (high-temperature flue gas generated by coal combustion). Under normal circumstances, the temperature of the coal-fired flue gas is 160-340 ° C, and the use of the heat to dry the raw coal can reduce the energy consumption. Moreover, the energy consumption of the microwave in the microwave desulfurization unit is not consumed, and the energy saving effect is achieved.
  • the system for desulfurizing and recovering elemental sulfur of the coal can not only remove the sulfur in the raw coal, but also recover the elemental sulfur product, and simultaneously desulfurize the coal-fired flue gas.
  • the system further includes a raw coal crushing unit connected to the feed port of the raw coal drying unit, or the raw coal drying unit is connected to the microwave desulfurization unit through the raw coal crushing unit.
  • the raw coal crushing unit comprises a crusher, preferably a ring hammer crusher and/or a hammer crusher.
  • the raw coal drying unit comprises a dryer.
  • Coal-fired flue gas can be introduced into the dryer through a first induced draft fan.
  • the pulverization and drying of raw coal and then microwave desulfurization can greatly reduce the energy loss of the microwave and the temperature of the raw coal.
  • the microwave reaction unit comprises a microwave reactor, wherein the microwave reactor is provided with an infrared temperature probe, a humidity sensor and a pressure sensor respectively connected to the centralized control system to control the temperature of the raw coal in the microwave reactor to prevent The coal is burned in a microwave reactor.
  • the microwave desulfurization unit further includes a microwave leakage suppression device disposed at a bottom and/or both sides of the microwave desulfurization unit; the microwave leakage suppression device is disposed at a microwave leakable position of the microwave desulfurization unit To prevent microwave leakage.
  • a microwave leakage suppression device disposed at a bottom and/or both sides of the microwave desulfurization unit; the microwave leakage suppression device is disposed at a microwave leakable position of the microwave desulfurization unit To prevent microwave leakage.
  • the microwave leakage suppression device is made of graphite and/or an alloy.
  • the microwave leakage suppressing device may also be made of other absorbing materials as long as it can prevent leakage of microwaves in the microwave desulfurization unit.
  • the system further includes a dust removing unit, wherein an air outlet of the exhaust gas collecting unit is connected to an air inlet of the elemental sulfur reaction unit through the dust removing unit; the dust removing unit is capable of collecting dust in the H2S-containing gas collected by the air collecting cover Remove 70-90%.
  • the dust removing unit comprises any one or a combination of at least two of a cyclone, an electrostatic precipitator or a bag filter.
  • a cyclone cyclones and electrostatic precipitators, electrostatic precipitators and bag filters.
  • the exhaust gas collecting unit comprises a gas collecting hood, and the top of the gas collecting hood is provided with a flow regulating valve and a gas component sensor.
  • the gas collecting hood is a closed gas collecting hood or a semi-closed gas collecting hood, and collects the dissipated gas by side suction or suction, in order to avoid the influence of the air flow on the feeding and discharging, the set
  • the movable side baffle is arranged at the connection between the hood and the microwave desulfurization unit, and the bottom baffle is designed with an oblique airflow distribution hole, which is favorable for the upward lifting of the airflow.
  • the elemental sulfur reaction unit comprises a sulfur reactor, in which a catalyst layer is provided, the catalyst layer comprising a pretreated Al 2 O 3 -based catalyst catalyst and/or a pretreated TiO 2 group Catalyst catalyst, pretreatment method includes redox treatment and/or roasting treatment, the pretreatment time is 1-5h, such as 1.5h, 2h, 2.5h, 3h, 3.5h, 4h or 4.5h, etc., the pretreatment temperature is 300- 600 ° C, such as 320 ° C, 330 ° C, 350 ° C, 380 ° C, 400 ° C, 420 ° C, 450 ° C, 500 ° C, 550 ° C or 580 ° C, etc., in order to increase the porosity and catalytic activity of the catalyst.
  • the redox treatment may be such that the catalyst can undergo a redox reaction.
  • the H 2 S-containing gas reacts with the coal-fired flue gas under the action of a catalyst, and the Claus reaction occurs in SO 2 and H 2 S in the flue gas (SO 2 +2H 2 S ⁇ 3S+2H 2 O+615kJ/mol ), the formation of elemental sulfur vapour, the elemental sulfur vapour after multi-stage condensation finally forms a sulfur by-product to achieve efficient recovery of elemental sulfur.
  • the elemental sulfur reaction unit further comprises a preheating device, and an air outlet of the exhaust gas collecting unit and an air outlet of the raw coal drying unit are connected to an air inlet of the sulfur reactor through the preheating device;
  • the thermal unit is used to heat the reaction gas to bring the temperature to the reaction temperature.
  • the temperature at which the H 2 S-containing gas reacts with SO 2 in the coal-fired flue gas is 200-400 ° C.
  • the preheating device comprises a heat exchanger.
  • the system further includes a condensing unit, the feeding port of the condensing unit is connected to the discharge port of the elemental sulfur reaction unit; and the condensing unit is used for cooling the elemental sulfur produced by the elemental sulfur reaction unit for storage.
  • the condensing unit comprises a multi-stage synergistic condenser, and a spiking thread structure is arranged in the condenser pipeline to promote condensation of low concentration sulfur vapor;
  • the system further includes a draft unit connected to an outlet of the elemental sulfur reaction unit; the lead unit is capable of withdrawing residual gas in the elemental sulfur reaction unit and discharging it into the atmosphere Or discharged into the atmosphere through the chimney.
  • the air guiding unit comprises a second induced draft fan.
  • Another object of the present invention is to provide a method for desulfurizing coal and recovering elemental sulfur, the method comprising the following steps:
  • the raw coal in the step (1) is crushed and then dried or dried, and then first broken and then subjected to microwave desulfurization.
  • the crushed raw coal has a particle diameter of 0.1 to 50 cm, such as 0.5 cm, 1 cm, 5 cm, 10 cm, 20 cm, 30 cm, 35 cm, 40 cm or 45 cm.
  • the mass percentage of water in the dried raw coal in the step (1) is 5% or less, such as 1%, 2%, 3%, 4% or 4.5%.
  • microwave desulfurization can greatly reduce the energy loss of the microwave.
  • the microwave frequency used in the microwave desulfurization in step (1) is 2500-2600 MHz, such as 2510 MHz, 2530 MHz, 2560 MHz, 2570 MHz or 2590 MHz, etc.
  • the microwave power is 300-500 W, such as 320 W, 350 W, 380 W, 400 W, 430 W, 450W or 480W, etc.
  • microwave desulfurization time is 1-5min, such as 2min, 3min, 4min or 4.5min.
  • the gas containing H 2 S in the step (2) is first dedusted and then reacted with the coal-fired flue gas after the heat exchange.
  • the dust removal efficiency is not less than 95%, such as 96%, 97%, 98% or 99%, and the like.
  • the temperature of the reaction in the step (2) is 200 to 400 ° C, such as 220 ° C, 250 ° C, 280 ° C, 300 ° C, 320 ° C, 350 ° C or 380 ° C.
  • the reaction in the step (2) is carried out under the catalysis of a pretreated Al 2 O 3 -based catalyst and/or a pretreated TiO 2 -based catalyst, and the pretreatment method comprises redox treatment and/or calcination.
  • Treatment, pretreatment time is 1-5h, such as 1.5h, 2h, 2.5h, 3h, 3.5h, 4h or 4.5h, etc.
  • the pretreatment temperature is 300-600 ° C, such as 320 ° C, 330 ° C, 350 ° C, 380 ° C, 400 ° C, 420 ° C, 450 ° C, 500 ° C, 550 ° C or 580 ° C, etc., to increase the porosity and catalytic activity of the catalyst.
  • the redox treatment may be such that the catalyst can undergo a redox reaction.
  • the method for desulfurizing coal and recovering elemental sulfur includes the following steps:
  • the coal-fired flue gas containing SO 2 is exchanged with the recovered raw coal to obtain dry raw coal with a water content of 5% or less and coal after heat exchange.
  • the coal-fired flue gas after heat exchange and the gas containing H 2 S are catalytically reacted at 200-400 ° C.
  • the catalyst is a pretreated Al 2 O 3 -based catalyst and/or pretreated TiO 2 based catalyst catalyst, redox treatment comprising a pretreatment and / or calcination treatment, pretreatment time is 1-5h, pretreatment temperature of 300-600 deg.] C, to give elemental sulfur product.
  • the method for desulfurizing coal and producing elemental sulfur provided by the invention not only saves energy consumption, but also can simultaneously treat exhaust gas and coal-fired flue gas generated by coal desulfurization, and has broad industrial application prospect.
  • the system and method for desulfurizing and recovering elemental sulfur provided by the invention have reasonable process design, strong operability, wide application range, safe and stable system, and can simultaneously remove and recover sulfur in coal.
  • the total sulfur content of coal is below 2.0%, and the total recovery rate of sulfur is not less than 40%.
  • the system and method for desulfurizing and recovering elemental sulfur provided by the invention have the advantages of compact process flow and small occupied area, and can be applied to coal desulfurization before combustion of coal-fired power plants, and utilizing waste heat of coal-fired boiler flue gas to pre-predetermine moisture in raw coal. Removal, reducing the consumption of microwave energy by moisture, achieving system-wide optimization and energy saving.
  • the system and method for desulfurizing coal and recovering elemental sulfur provided by the invention, and arranging the H 2 S of the high sulfur coal heat by the catalyst to catalyze the release of the SO 2 in the coal combustion flue gas, thereby eliminating the H 2 in the traditional sulfur recovery process.
  • the generated sulfur element can be sold as a by-product after purification, and has good environmental and economic benefits.
  • the microwave desulfurization process adopts infrared temperature measurement and installs a microwave leakage suppression device to ensure the safety of the system operation, and the microwave reactor operates under a negative pressure to avoid pollutants from escaping. .
  • Example 1 is a schematic view showing the structure of a system for desulfurizing coal and recovering elemental sulfur provided in Example 1.
  • a system for desulfurizing high sulfur coal and recovering elemental sulfur as shown in Figure 1, the system comprising:
  • a raw coal crushing unit for crushing raw coal including a crusher 1, preferably a crusher 1 and/or a hammer crusher 1;
  • Raw coal drying unit for drying raw coal including dryer 2;
  • a microwave desulfurization unit for microwave desulfurization of coal comprising a microwave reactor 5, wherein the microwave reactor 5 is provided with an infrared temperature probe 4, a humidity sensor and a pressure sensor connected to the control system; the microwave desulfurization unit further comprises a microwave leakage suppression device 6, which is made of graphite and/or an alloy, and the microwave leakage suppression device 6 is disposed at the bottom and/or both sides of the microwave desulfurization unit;
  • the exhaust gas collecting unit is configured to collect the H 2 S-containing gas generated by the microwave desulfurization unit, and includes a gas collecting cover 7 .
  • the gas collecting cover 7 is provided with a flow regulating valve and a gas component sensor at the top, and the gas collecting cover 7 is sealed.
  • a movable side baffle is arranged at a joint of the gas collecting hood 7 and the microwave reactor 5, and a bottom air flow distribution hole is arranged at the bottom of the side baffle;
  • a dust removing unit for dedusting a gas containing H 2 S including any one or a combination of at least two of a cyclone 8, an electrostatic precipitator 8 or a baghouse 8;
  • An elemental sulfur reaction unit for reacting the H 2 S-containing gas with the SO 2 -containing coal-fired flue gas to produce elemental sulfur including a sulfur reactor 10 and a heat exchanger 9, the sulfur reaction
  • the catalyst layer 10 is provided in the catalyst 10, the catalyst layer comprises a pretreated Al 2 O 3 -based catalyst catalyst and/or a pretreated TiO 2 -based catalyst catalyst, and the pretreatment method comprises a redox treatment and/or a roasting treatment,
  • the treatment time is 1-5h, such as 1.5h, 2h, 2.5h, 3h, 3.5h, 4h or 4.5h, etc.
  • the pretreatment temperature is 300-600 °C, such as 320 °C, 330 °C, 350 °C, 380 °C, 400 °C, 420 ° C, 450 ° C, 500 ° C, 550 ° C or 580 ° C, etc.;
  • a condensing unit for condensing high-temperature elemental sulfur produced by the sulfur elemental sulfur reaction unit comprising a condenser 11, the condenser 11 being a multi-stage condenser, such as a 2-stage condenser, a 3-stage condenser, a 5-stage condenser or 10 Stage condenser, etc., a spiked thread structure is arranged in the condenser line;
  • a draft unit for extracting unreacted gas in the elemental sulfur reaction unit comprising a second induced draft fan 12;
  • the coal-fired flue gas is introduced into the dryer 2 through the first induced draft fan 3;
  • the crusher 1, the dryer 2 and the microwave reactor 5 are connected in sequence, and the gas collecting cover 7 is disposed at the gas outlet of the microwave reactor 5, and the gas outlet of the gas collecting cover 7 passes through the dust remover 8 and the heat exchanger.
  • 9 is connected to the inlet of the sulfur reactor 10
  • the outlet of the coal-fired furnace is connected to the inlet of the sulfur reactor 10 through the dryer 2 and the heat exchanger 9, and the inlet of the condenser 11 and the sulfur reactor
  • the discharge port of 10 is connected; the second induced draft fan 12 is disposed between the sulfur reactor 10 and the chimney 13.
  • a process for desulfurizing high-sulfur coal and producing elemental sulfur is as follows: the raw coal conveyed by the coal storage bin enters the crusher 1, and the raw coal is broken into a particle size of 0.1-50 cm, and the crushed raw coal enters the dryer 2 by heat The coal-fired flue gas is dried and dehydrated to reduce the moisture in the raw coal to less than 5%.
  • the dried raw coal is transported to the microwave reactor 5 by a continuous conveyor belt, and irradiated in a microwave of 2500-2600 MHz and a power of 300-500 W. 5 min, the raw coal after desulfurization is ground to the coal mill for grinding and then injected into the boiler for combustion;
  • the dust, H 2 S, SO 2 flue gas generated by the microwave pyrolysis of the raw coal is collected by the gas collecting hood 7 and then enters the dust collector 8 , and the dust collector 8 collects the dust, and the dust collecting efficiency is not less than 95%.
  • the captured dust ash is transported to the pulverized coal bin for reuse; the flue gas after dust removal is mixed with the hot flue gas after the dryer 2, and is heated by the heat exchanger 9 to enter the sulfur reactor 10, and the catalyst is catalyzed by the catalyst.
  • Sulfur elemental vapor is produced under the reaction temperature of 200-400 ° C, and the elemental sulfur vapor is condensed by multiple stages to form a sulfur by-product, thereby achieving efficient recovery of elemental sulfur.
  • the high sulfur coal desulfurization test was carried out by the method of desulfurizing high sulfur coal of Example 1 and producing elemental sulfur.
  • the details are as follows: in the 1000MW coal-fired power plant, the coal consumption is 360t/h, the sulfur content in the high-sulfur raw coal is 3.56%, the moisture content is 6.11%, and the particle size is 20-35cm after crushing, and the induced draft fan will be 240.
  • °C boiler flue gas is introduced into the front end of the dryer.
  • the SO 2 content in the flue gas is 2000mg/Nm 3
  • the O 2 content is 6%
  • the flue gas flow rate is 15 ⁇ 10 4 Nm 3 /h
  • the moisture content of the raw coal after drying is reduced.
  • the outlet flue gas temperature drops to 180 °C
  • the raw coal after drying enters the conveyor belt
  • the conveyor belt conveys 50t/h
  • the raw coal enters the microwave reactor, and is irradiated for 3min in 2540MHz, 300W microwave, desulfurization
  • the sulfur content in the post coal was reduced to 1.44%
  • the total desulfurization efficiency (the total desulfurization efficiency in the present invention is the ratio of the reduction before and after the sulfur content unless otherwise specified) was 59.5%.
  • the dust and H 2 S pollutants generated by microwave irradiation and raw coal transportation are collected by the gas collecting hood.
  • the gas flow rate of the gas collecting hood is 8m/s, the gas flow rate is 15 ⁇ 10 4 m 3 /h, and the O 2 content is 20. %, H2S concentration is 708mg/m 3 , gas temperature is 120 ° C, the flue gas and boiler flue gas are mixed and heat-treated to 340 ° C, reacted under the action of catalyst, sulfur elemental conversion rate is 95%, total The sulfur recovery rate was 56.5%, and the sulfur element was 2.85 t/h.
  • Example 1 the high sulfur coal desulfurization test was carried out by the method of desulfurizing high sulfur coal of Example 1 and producing elemental sulfur. The details are as follows: in the 500MW coal-fired power plant, the coal consumption is 200t/h, the sulfur content in the high-sulfur raw coal is 6.24%, the moisture content is 7.21%, and the crusher is crushed to a particle size of 15-30cm, and the induced draft fan will be 280. °C boiler flue gas is introduced into the front end of the dryer.
  • the SO 2 content in the flue gas is 4000mg/Nm 3 , the O 2 content is 6%, the flue gas flow rate is 10 ⁇ 10 4 Nm 3 /h, and the moisture content of the raw coal after drying is reduced. 4.61%, the outlet flue gas temperature drops to 160 ° C, the raw coal after drying enters the conveyor belt, the conveyor belt transport volume is 30t / h, the raw coal enters the microwave reactor, irradiated in the microwave at 2540MHz, power 500W for 5min, desulfurization The sulfur content in the post coal was reduced to 1.52%, and the total desulfurization efficiency was 75.6%.
  • the dust and H 2 S pollutants generated by microwave irradiation and raw coal transportation are collected by the gas collecting hood.
  • the gas flow rate of the gas collecting hood is 10m/s, the gas flow rate is 8 ⁇ 10 4 m 3 /h, and the O 2 content is 18 %, H 2 S concentration is 17708mg / m 3 , gas temperature is 130 ° C, the flue gas and boiler flue gas mixed after heat exchange, the temperature is raised to 400 ° C, the reaction under the action of the catalyst, the sulfur elemental conversion rate is 96% The total sulfur recovery rate was 72.6%, and the sulfur production was 3.84t/h.
  • the high sulfur coal desulfurization test was carried out by the method of desulfurizing high sulfur coal of Example 1 and producing elemental sulfur.
  • the details are as follows: in the 300MW coal-fired power plant, the coal consumption is 150t/h, the sulfur content in the high-sulfur raw coal is 3.15%, the moisture content is 5.12%, and the particle size is 40-50cm after crushing, and the induced draft fan will be 260.
  • °C boiler flue gas is introduced into the front end of the dryer.
  • the SO 2 content in the flue gas is 1500mg/Nm 3 , the O 2 content is 6%, the flue gas flow rate is 5 ⁇ 10 4 Nm 3 /h, and the moisture content of the raw coal after drying is reduced.
  • the outlet flue gas temperature drops to 160 °C
  • the raw coal after drying enters the conveyor belt
  • the conveyor belt conveys 30t/h
  • the raw coal enters the microwave reactor, and is irradiated for 2min in 2500MHz, 300W microwave, desulfurization
  • the sulfur content in the post coal was reduced to 1.38%, and the total desulfurization efficiency was 56.2%.
  • the dust and H 2 S pollutants generated by microwave irradiation and raw coal transportation are collected by the gas collecting hood.
  • the gas flow rate of the gas collecting hood is 10m/s, the gas flow rate is 5 ⁇ 10 4 m 3 /h, and the O 2 content is 18 %, H 2 S concentration is 5312mg / m 3 , gas temperature is 140 ° C, the flue gas and boiler flue gas mixed heat exchange and then heated to 200 ° C, the reaction under the action of the catalyst, sulfur elemental conversion rate of 92%
  • the total sulfur recovery rate was 51.7%, and the sulfur production was 0.69 t/h.
  • the high sulfur coal desulfurization test was carried out by the method of desulfurizing high sulfur coal of Example 1 and producing elemental sulfur.
  • the details are as follows: in the 600MW coal-fired power plant, the coal consumption is 250t/h, the sulfur content in the high-sulfur raw coal is 2.65%, the moisture content is 5.17%, and the particle size is 10-50mm after crushing, and the induced draft fan will be 300.
  • °C boiler flue gas is introduced into the front end of the dryer.
  • the SO 2 content in the flue gas is 1000mg/Nm 3 , the O 2 content is 6%, the flue gas flow rate is 8 ⁇ 10 4 Nm 3 /h, and the moisture content of the raw coal after drying is reduced.
  • the outlet flue gas temperature drops to 150 ° C
  • the raw coal after drying enters the conveyor belt
  • the conveyor belt transport volume is 30t / h
  • the raw coal enters the microwave reactor, irradiated in the microwave at 2600MHz, power 400W for 2min
  • desulfurization The sulfur content in the post coal was reduced to 1.51%, and the total desulfurization efficiency was 43.0%.
  • the dust and H 2 S pollutants generated by microwave irradiation and raw coal transportation are collected by the gas collecting hood.
  • the gas flow rate of the gas collecting hood is 10m/s, the gas flow rate is 5 ⁇ 10 4 m 3 /h, and the O 2 content is 18 %, H 2 S concentration is 5666mg / m 3 , gas temperature is 120 ° C, the flue gas and boiler flue gas mixed after heat exchange, the temperature is raised to 300 ° C, the reaction under the action of the catalyst, the sulfur elemental conversion rate is 95%
  • the total sulfur recovery rate is 40.85%, and the sulfur production is 0.76t/h.
  • the catalysts of Examples 2-5 were selected from the pretreated Al 2 O 3 -based catalysts, which were calcined at a calcination time of 3 h and a calcination temperature of 500 °C.
  • the catalyst of Examples 2-5 may also be selected from a pretreated Al 2 O 3 -based catalyst catalyst and/or a pretreated TiO 2 -based catalyst catalyst other than the above catalysts, the pretreatment method including redox treatment and/or Or roasting treatment, the pretreatment time is 1-5h, such as 1.5h, 2h, 2.5h, 3.5h, 4h or 4.5h, etc., the pretreatment temperature is 300-600 ° C, such as 320 ° C, 330 ° C, 350 ° C, 380 ° C, 400 ° C, 420 ° C, 450 ° C, 550 ° C or 580 ° C and so on.

Abstract

A system and a method for desulfurizing coal and recovering elemental sulfur. The system comprises a microwave desulfurization unit, and further comprises a raw coal drying unit, an exhaust gas collecting unit, and an elemental sulfur reaction unit, a discharge port of the raw coal drying unit being connected to a feed port of the microwave desulfurization unit, the exhaust gas collecting unit being disposed at an air outlet of the microwave desulfurization unit, and an air inlet of the elemental sulfur reaction unit being respectively connected to an air outlet of the raw coal drying unit and an air outlet of the exhaust gas collecting unit. The system and method can simultaneously remove and recover sulfur from coal, producing treated coal with a total sulfur content of less than 2.0%, and a total recovery rate of elemental sulfur of not less than 40%. The system and the method are safe and energy-saving and are suitable for desulfurization and sulfur recovery of medium- and high-sulfur coals of varying quality.

Description

一种煤炭脱硫并回收单质硫的系统及方法System and method for desulfurizing coal and recovering elemental sulfur 技术领域Technical field
本发明属于煤炭清洁化技术领域,涉及一种煤炭脱硫并回收生产单质硫的系统及方法。The invention belongs to the technical field of coal cleaning, and relates to a system and a method for desulfurizing coal and recovering and producing elemental sulfur.
背景技术Background technique
我国煤炭资源丰富,煤炭中硫含量平均为1.72%,其中高硫煤(S含量≥2.0%,包括高硫煤和中硫煤)探明储量约占煤炭总储量的1/3,占原煤生产的16.67%,具有巨大的潜在应用价值。China's coal resources are abundant, and the sulfur content in coal is 1.72% on average. Among them, high-sulfur coal (S content ≥2.0%, including high-sulfur coal and medium-sulfur coal) has about 1/3 of the total reserves of coal, accounting for the production of raw coal. 16.67% has great potential application value.
高硫煤中蕴藏着巨大的硫资源,2016年我国原煤产量共计33.64吨,按煤中S含量为2.0%计算,高硫煤所含的S含量在1121万吨;2016年我国硫磺产量仅为516万吨,进口硫磺为1196.1万吨,对外依存度超过50%,而我国目前高硫煤的使用及硫回收水平低,从煤中回收的硫磺数量很少。此外,高硫煤不经过任何处理直接进行燃烧会造成大量SO2排放,对环境造成严重污染,因此急需开发一种经济可行的高硫煤脱硫及硫资源化回收的技术和方法。There are huge sulfur resources in high-sulfur coal. In 2016, China's raw coal production totaled 33.64 tons. According to the S content of coal, which is 2.0%, the high-sulfur coal contains S 11.1 million tons. In 2016, China's sulfur production is only 5.16 million tons, imported sulfur is 11.961 million tons, and the external dependence is more than 50%. However, the use of high-sulfur coal and low sulfur recovery in China is low, and the amount of sulfur recovered from coal is very small. In addition, high-sulfur coal directly burned without any treatment will cause a large amount of SO 2 emissions and cause serious pollution to the environment. Therefore, it is urgent to develop an economically viable technology and method for high-sulfur coal desulfurization and sulfur resource recovery.
利用微波脱硫是近年来高硫煤脱硫的新方法,微波是频率在0.3-300GHz,波长在1mm-100cm的电磁波,煤中的黄铁矿等无机硫在微波下分解,主要释放出H2S,H2S与少量的SO2在煤表面生成单质硫,黄铁矿在高温的作用下转变为磁性黄铁矿,这种方法可以脱除煤中约50%的硫。US4076607最早提出了这一方法,CN206051972A(一种用于高硫煤脱硫的微波预处理装置)、CN102816623A(一种微波低温脱水及脱硫的煤炭提质装置)及CN105623775A(一种利用微波热解脱除煤矸石中汞、硫、氮的方法)等均采用了微波辐射对煤炭/煤矸石中的硫进行脱除,但上述方法只考虑了煤炭中硫的释放方法,普遍 忽略了对反应后逸出气体的收集和硫的回收,受限于反应器类型,已有的专利或未能实现连续生产,或未考虑微波处理过程温度、微波泄漏等安全问题。The use of microwave desulfurization is a new method for desulfurization of high-sulfur coal in recent years. The microwave is an electromagnetic wave with a frequency of 0.3-300 GHz and a wavelength of 1 mm-100 cm. The inorganic sulfur such as pyrite in the coal is decomposed under microwave, mainly releasing H 2 S. H 2 S and a small amount of SO 2 form elemental sulfur on the coal surface, and pyrite is converted into magnetic pyrite under the action of high temperature. This method can remove about 50% of sulfur in coal. US4076607 first proposed this method, CN206051972A (a microwave pretreatment device for high sulfur coal desulfurization), CN102816623A (a microwave upgrading device for microwave low temperature dehydration and desulfurization) and CN105623775A (a microwave thermal desorption method) In addition to mercury, sulfur, and nitrogen in coal gangue, microwaves are used to remove sulfur from coal/gangue. However, the above method only considers the release method of sulfur in coal, and generally ignores the reaction after the reaction. The collection of gas and the recovery of sulfur are limited by the type of reactor, existing patents or failure to achieve continuous production, or safety issues such as microwave processing temperature and microwave leakage are not considered.
发明内容Summary of the invention
针对现有技术存在的问题,本发明的目的在于提供一种煤炭脱硫并回收单质硫的系统及方法,该系统及方法能够同时对煤炭中的硫进行脱除和回收,使煤中总含硫量控制在2.0%以下,硫单质总回收率不低于40%,安全节能,适用于各种煤质高硫煤脱硫及硫的回收。In view of the problems existing in the prior art, the present invention aims to provide a system and method for desulfurizing coal and recovering elemental sulfur, which can simultaneously remove and recover sulfur in coal to make total sulfur in coal. The quantity control is below 2.0%, the total recovery rate of sulfur element is not less than 40%, safe and energy saving, suitable for desulfurization and sulfur recovery of various coal high-sulfur coal.
为达此目的,本发明采用以下技术方案:To this end, the present invention employs the following technical solutions:
本发明的目的之一在于提供一种煤炭脱硫并回收单质硫的系统,包括微波脱硫单元,还包括:One of the objects of the present invention is to provide a system for desulfurizing coal and recovering elemental sulfur, including a microwave desulfurization unit, and further comprising:
原煤烘干单元,用于含有SO2的燃煤烟气对煤炭的烘干,得到干燥的煤炭并排出换热后的燃煤烟气;Coal drying unit, for containing SO 2 from flue gas for coal drying, the resulting dried coal and flue gas discharged after heat exchange;
废气收集单元,用于收集微波脱硫单元产生的含有H2S的气体;An exhaust gas collecting unit for collecting the H 2 S-containing gas generated by the microwave desulfurization unit;
单质硫反应单元,用于所述含有H2S的气体与所述换热后的燃煤烟气之间的反应,产生单质硫;An elemental sulfur reaction unit for reacting between the H 2 S-containing gas and the heat-exchanged coal-fired flue gas to produce elemental sulfur;
其中,所述原煤烘干单元的出料口与微波脱硫单元的进料口相连,所述废气收集单元设置于所述微波脱硫单元的出气口处,单质硫反应单元的进气口分别与原煤烘干单元的出气口和废气收集单元的出气口相连。Wherein, the discharge port of the raw coal drying unit is connected to the feed port of the microwave desulfurization unit, the exhaust gas collection unit is disposed at the air outlet of the microwave desulfurization unit, and the air inlet of the elemental sulfur reaction unit is respectively separated from the raw coal The air outlet of the drying unit is connected to the air outlet of the exhaust gas collection unit.
原煤烘干单元利用燃煤烟气(煤炭燃烧产生的高温烟气)的余热烘干的,一般情况下燃煤烟气的温度为160-340℃,利用其热量烘干原煤能够降低能耗,并且不消耗微波脱硫单元中微波的能耗,起到节能的作用。The raw coal drying unit is dried by the waste heat of coal-fired flue gas (high-temperature flue gas generated by coal combustion). Under normal circumstances, the temperature of the coal-fired flue gas is 160-340 ° C, and the use of the heat to dry the raw coal can reduce the energy consumption. Moreover, the energy consumption of the microwave in the microwave desulfurization unit is not consumed, and the energy saving effect is achieved.
所述煤炭脱硫并回收单质硫的系统不但能够将原煤中的硫脱除,还能够回收单质硫产品,并且能够同时对燃煤烟气脱硫。 The system for desulfurizing and recovering elemental sulfur of the coal can not only remove the sulfur in the raw coal, but also recover the elemental sulfur product, and simultaneously desulfurize the coal-fired flue gas.
所述系统还包括原煤破碎单元,所述原煤破碎单元与原煤烘干单元的进料口相连,或所述原煤烘干单元通过原煤破碎单元与微波脱硫单元相连。The system further includes a raw coal crushing unit connected to the feed port of the raw coal drying unit, or the raw coal drying unit is connected to the microwave desulfurization unit through the raw coal crushing unit.
优选地,所述原煤破碎单元包括破碎机,所述破碎机优选为环锤式破碎机和/或锤式破碎机。Preferably, the raw coal crushing unit comprises a crusher, preferably a ring hammer crusher and/or a hammer crusher.
优选地,所述原煤烘干单元包括烘干器。燃煤烟气可通过第一引风机引入所述烘干器中。Preferably, the raw coal drying unit comprises a dryer. Coal-fired flue gas can be introduced into the dryer through a first induced draft fan.
将原煤粉碎并烘干后再进行微波脱硫能够大大降低微波的能量损耗和原煤温度。The pulverization and drying of raw coal and then microwave desulfurization can greatly reduce the energy loss of the microwave and the temperature of the raw coal.
优选地,所述微波反应单元包括微波反应器,所述微波反应器内设置有与集中控制系统分别相连的红外测温探头、湿度传感器和压力传感器,以控制微波反应器中原煤的温度,防止煤在微波反应器中燃烧。Preferably, the microwave reaction unit comprises a microwave reactor, wherein the microwave reactor is provided with an infrared temperature probe, a humidity sensor and a pressure sensor respectively connected to the centralized control system to control the temperature of the raw coal in the microwave reactor to prevent The coal is burned in a microwave reactor.
优选地,所述微波脱硫单元还包括微波泄漏抑制装置,所述微波泄漏抑制装置设置于微波脱硫单元的底部和/或两侧;所述微波泄漏抑制装置设置在微波脱硫单元的微波可泄漏位置,防止微波的泄漏。Preferably, the microwave desulfurization unit further includes a microwave leakage suppression device disposed at a bottom and/or both sides of the microwave desulfurization unit; the microwave leakage suppression device is disposed at a microwave leakable position of the microwave desulfurization unit To prevent microwave leakage.
优选地,所述微波泄漏抑制装置由石墨和/或合金制成。所述微波泄漏抑制装置也可由其它的吸波材料制成,只要其能够防止微波脱硫单元中微波的泄漏即可。Preferably, the microwave leakage suppression device is made of graphite and/or an alloy. The microwave leakage suppressing device may also be made of other absorbing materials as long as it can prevent leakage of microwaves in the microwave desulfurization unit.
所述系统还包括除尘单元,所述废气收集单元的出气口通过所述除尘单元与单质硫反应单元的进气口相连;所述除尘单元能够将集气罩收集的含有H2S的气体中的粉尘去除70-90%。The system further includes a dust removing unit, wherein an air outlet of the exhaust gas collecting unit is connected to an air inlet of the elemental sulfur reaction unit through the dust removing unit; the dust removing unit is capable of collecting dust in the H2S-containing gas collected by the air collecting cover Remove 70-90%.
优选地,所述除尘单元包括旋风除尘器、静电除尘器或布袋式除尘器中的任意一种或至少两种的组合。典型但非限制性的组合如旋风除尘器与静电除尘器,静电除尘器与布袋除尘器等。 Preferably, the dust removing unit comprises any one or a combination of at least two of a cyclone, an electrostatic precipitator or a bag filter. Typical but non-limiting combinations are cyclones and electrostatic precipitators, electrostatic precipitators and bag filters.
优选地,所述废气收集单元包括集气罩,所述集气罩顶部设置流量调节阀和气体组分传感器。Preferably, the exhaust gas collecting unit comprises a gas collecting hood, and the top of the gas collecting hood is provided with a flow regulating valve and a gas component sensor.
优选地,所述集气罩为密闭式集气罩或半密闭式集气罩,通过侧吸或者顶吸的方式对逸散的气体进行收集,为避免气流对进出料的影响,所述集气罩与微波脱硫单元的连接处设置活动侧挡板,侧挡板底部设计有斜气流分布孔,利于气流的向上抬升。Preferably, the gas collecting hood is a closed gas collecting hood or a semi-closed gas collecting hood, and collects the dissipated gas by side suction or suction, in order to avoid the influence of the air flow on the feeding and discharging, the set The movable side baffle is arranged at the connection between the hood and the microwave desulfurization unit, and the bottom baffle is designed with an oblique airflow distribution hole, which is favorable for the upward lifting of the airflow.
优选地,所述单质硫反应单元包括硫反应器,所述硫反应器中设置催化剂层,所述催化剂层包括经过预处理的Al2O3基触媒催化剂和/或经过预处理的TiO2基触媒催化剂,预处理方法包括氧化还原处理和/或焙烧处理,预处理时间为1-5h,如1.5h、2h、2.5h、3h、3.5h、4h或4.5h等,预处理温度为300-600℃,如320℃、330℃、350℃、380℃、400℃、420℃、450℃、500℃、550℃或580℃等,以提高催化剂的孔隙度和催化活性。所述氧化还原处理只要能够使得所述催化剂发生氧化还原反应即可。Preferably, the elemental sulfur reaction unit comprises a sulfur reactor, in which a catalyst layer is provided, the catalyst layer comprising a pretreated Al 2 O 3 -based catalyst catalyst and/or a pretreated TiO 2 group Catalyst catalyst, pretreatment method includes redox treatment and/or roasting treatment, the pretreatment time is 1-5h, such as 1.5h, 2h, 2.5h, 3h, 3.5h, 4h or 4.5h, etc., the pretreatment temperature is 300- 600 ° C, such as 320 ° C, 330 ° C, 350 ° C, 380 ° C, 400 ° C, 420 ° C, 450 ° C, 500 ° C, 550 ° C or 580 ° C, etc., in order to increase the porosity and catalytic activity of the catalyst. The redox treatment may be such that the catalyst can undergo a redox reaction.
所述含有H2S的气体与燃煤烟气在触媒的作用下,烟气中SO2和H2S发生克劳斯反应(SO2+2H2S→3S+2H2O+615kJ/mol),生成单质硫蒸气,单质硫蒸气经过多级冷凝最后形成硫磺副产品,实现单质硫的高效回收。The H 2 S-containing gas reacts with the coal-fired flue gas under the action of a catalyst, and the Claus reaction occurs in SO 2 and H 2 S in the flue gas (SO 2 +2H 2 S→3S+2H 2 O+615kJ/mol ), the formation of elemental sulfur vapour, the elemental sulfur vapour after multi-stage condensation finally forms a sulfur by-product to achieve efficient recovery of elemental sulfur.
优选地,所述单质硫反应单元还包括预热装置,所述废气收集单元的出气口和原煤烘干单元的出气口通过所述预热装置与硫反应器的进气口相连;所述预热单元用于加热反应气体,使其温度达到反应温度。所述含有H2S的气体与燃煤烟气中的SO2进行反应的温度为200-400℃。Preferably, the elemental sulfur reaction unit further comprises a preheating device, and an air outlet of the exhaust gas collecting unit and an air outlet of the raw coal drying unit are connected to an air inlet of the sulfur reactor through the preheating device; The thermal unit is used to heat the reaction gas to bring the temperature to the reaction temperature. The temperature at which the H 2 S-containing gas reacts with SO 2 in the coal-fired flue gas is 200-400 ° C.
优选地,所述预热装置包括换热器。Preferably, the preheating device comprises a heat exchanger.
所述系统还包括冷凝单元,所述冷凝单元的进料口与单质硫反应单元的出料口相连;所述冷凝单元用于将单质硫反应单元生产的硫单质冷却,便于储存。 The system further includes a condensing unit, the feeding port of the condensing unit is connected to the discharge port of the elemental sulfur reaction unit; and the condensing unit is used for cooling the elemental sulfur produced by the elemental sulfur reaction unit for storage.
优选地,所述冷凝单元包括多级增效冷凝器,冷凝器管路内设置尖刺螺纹结构,促进低浓度硫蒸气冷凝;Preferably, the condensing unit comprises a multi-stage synergistic condenser, and a spiking thread structure is arranged in the condenser pipeline to promote condensation of low concentration sulfur vapor;
优选地,所述系统还包括引风单元,所述引风单元连接于所述单质硫反应单元的出气口处;所述引风单元能够将单质硫反应单元中的剩余气体引出,排入大气或通过烟囱排入大气。Preferably, the system further includes a draft unit connected to an outlet of the elemental sulfur reaction unit; the lead unit is capable of withdrawing residual gas in the elemental sulfur reaction unit and discharging it into the atmosphere Or discharged into the atmosphere through the chimney.
优选地,所述引风单元包括第二引风机。Preferably, the air guiding unit comprises a second induced draft fan.
本发明的目的之二在于提供一种煤炭脱硫并回收单质硫的方法,所述方法包括如下步骤:Another object of the present invention is to provide a method for desulfurizing coal and recovering elemental sulfur, the method comprising the following steps:
(1)采用含有SO2的燃煤烟气将原煤烘干,得到干燥的原煤和换热后的燃煤烟气;干燥的原煤进行微波脱硫,得到含有H2S的气体;(1) drying the raw coal with coal-fired flue gas containing SO 2 to obtain dried raw coal and coal-fired flue gas after heat exchange; the dried raw coal is subjected to microwave desulfurization to obtain a gas containing H 2 S;
(2)含有H2S的气体与换热后的燃煤烟气进行反应,生成单质硫。(2) The gas containing H2S reacts with the coal-fired flue gas after heat exchange to form elemental sulfur.
步骤(1)所述原煤经破碎后再进行烘干或烘干后先破碎再进行微波脱硫。The raw coal in the step (1) is crushed and then dried or dried, and then first broken and then subjected to microwave desulfurization.
优选地,破碎后的原煤的粒径为0.1-50cm,如0.5cm、1cm、5cm、10cm、20cm、30cm、35cm、40cm或45cm等。Preferably, the crushed raw coal has a particle diameter of 0.1 to 50 cm, such as 0.5 cm, 1 cm, 5 cm, 10 cm, 20 cm, 30 cm, 35 cm, 40 cm or 45 cm.
优选地,步骤(1)所述干燥的原煤中水的质量百分含量为5%以下,如1%、2%、3%、4%或4.5%等。Preferably, the mass percentage of water in the dried raw coal in the step (1) is 5% or less, such as 1%, 2%, 3%, 4% or 4.5%.
将原煤破碎及烘干后再进行微波脱硫能够大大降低微波的能量损失。After the raw coal is crushed and dried, microwave desulfurization can greatly reduce the energy loss of the microwave.
优选地,步骤(1)所述微波脱硫使用的微波频率为2500-2600MHz,如2510MHz、2530MHz、2560MHz、2570MHz或2590MHz等,微波功率为300-500W,如320W、350W、380W、400W、430W、450W或480W等,微波脱硫时间为1-5min,如2min、3min、4min或4.5min等。Preferably, the microwave frequency used in the microwave desulfurization in step (1) is 2500-2600 MHz, such as 2510 MHz, 2530 MHz, 2560 MHz, 2570 MHz or 2590 MHz, etc., and the microwave power is 300-500 W, such as 320 W, 350 W, 380 W, 400 W, 430 W, 450W or 480W, etc., microwave desulfurization time is 1-5min, such as 2min, 3min, 4min or 4.5min.
步骤(2)所述含有H2S的气体先除尘再与换热后的燃煤烟气进行反应。The gas containing H 2 S in the step (2) is first dedusted and then reacted with the coal-fired flue gas after the heat exchange.
优选地,所述除尘效率不低于95%,如96%、97%、98%或99%等。 Preferably, the dust removal efficiency is not less than 95%, such as 96%, 97%, 98% or 99%, and the like.
步骤(2)所述反应的温度为200-400℃,如220℃、250℃、280℃、300℃、320℃、350℃或380℃等。The temperature of the reaction in the step (2) is 200 to 400 ° C, such as 220 ° C, 250 ° C, 280 ° C, 300 ° C, 320 ° C, 350 ° C or 380 ° C.
优选地,步骤(2)所述反应在经过预处理的Al2O3基触媒催化剂和/或经过预处理的TiO2基触媒催化剂的催化下进行,预处理方法包括氧化还原处理和/或焙烧处理,预处理时间为1-5h,如1.5h、2h、2.5h、3h、3.5h、4h或4.5h等,预处理的温度为300-600℃,如320℃、330℃、350℃、380℃、400℃、420℃、450℃、500℃、550℃或580℃等,以提高催化剂的孔隙度和催化活性。所述氧化还原处理只要能够使得所述催化剂发生氧化还原反应即可。Preferably, the reaction in the step (2) is carried out under the catalysis of a pretreated Al 2 O 3 -based catalyst and/or a pretreated TiO 2 -based catalyst, and the pretreatment method comprises redox treatment and/or calcination. Treatment, pretreatment time is 1-5h, such as 1.5h, 2h, 2.5h, 3h, 3.5h, 4h or 4.5h, etc., the pretreatment temperature is 300-600 ° C, such as 320 ° C, 330 ° C, 350 ° C, 380 ° C, 400 ° C, 420 ° C, 450 ° C, 500 ° C, 550 ° C or 580 ° C, etc., to increase the porosity and catalytic activity of the catalyst. The redox treatment may be such that the catalyst can undergo a redox reaction.
作为优优选的技术方案,所述煤炭脱硫并回收单质硫的方法包括如下步骤:As a preferred technical solution, the method for desulfurizing coal and recovering elemental sulfur includes the following steps:
(1)将原煤破碎至0.1-50cm后,利用含有SO2的燃煤烟气与破碎后的原煤换热,得到水的质量百分含量为5%以下的干燥原煤和换热后的燃煤烟气;干燥原煤进行微波脱硫,微波的频率为2500-2600MHz,微波功率为300-500W,微波脱硫时间为1-5min,得到含有H2S的气体;(1) After the raw coal is crushed to 0.1-50cm, the coal-fired flue gas containing SO 2 is exchanged with the recovered raw coal to obtain dry raw coal with a water content of 5% or less and coal after heat exchange. Flue gas; dry raw coal for microwave desulfurization, microwave frequency is 2500-2600MHz, microwave power is 300-500W, microwave desulfurization time is 1-5min, and gas containing H 2 S is obtained;
(2)换热后的燃煤烟气与含有H2S的气体在200-400℃条件下进行催化反应,催化剂为经过预处理的Al2O3基触媒催化剂和/或经过预处理的TiO2基触媒催化剂,预处理方法包括氧化还原处理和/或焙烧处理,预处理时间为1-5h,预处理温度为300-600℃,得到单质硫产品。(2) The coal-fired flue gas after heat exchange and the gas containing H 2 S are catalytically reacted at 200-400 ° C. The catalyst is a pretreated Al 2 O 3 -based catalyst and/or pretreated TiO 2 based catalyst catalyst, redox treatment comprising a pretreatment and / or calcination treatment, pretreatment time is 1-5h, pretreatment temperature of 300-600 deg.] C, to give elemental sulfur product.
本发明提供的煤脱硫并生产单质硫的方法,不但节约能耗,而且能够同时处理煤脱硫产生的废气和燃煤烟气,其具有广阔的工业应用前景。The method for desulfurizing coal and producing elemental sulfur provided by the invention not only saves energy consumption, but also can simultaneously treat exhaust gas and coal-fired flue gas generated by coal desulfurization, and has broad industrial application prospect.
与现有技术相比,本发明的有益效果为:Compared with the prior art, the beneficial effects of the present invention are:
1、本发明提供的煤炭脱硫并回收单质硫的系统及方法,工艺设计合理,可操作性性强,适用范围广,系统安全稳定,能同时对煤炭中硫进行脱除和回收,处理后的煤炭总含硫量在2.0%以下,硫单质总回收率不低于40%。 1. The system and method for desulfurizing and recovering elemental sulfur provided by the invention have reasonable process design, strong operability, wide application range, safe and stable system, and can simultaneously remove and recover sulfur in coal. The total sulfur content of coal is below 2.0%, and the total recovery rate of sulfur is not less than 40%.
2、本发明提供的煤炭脱硫并回收单质硫的系统及方法,工艺流程紧凑,占地面积小,可适用于燃煤电厂燃烧前煤炭脱硫,利用燃煤锅炉烟气余热对原煤中水分进行预脱除,降低了水分对微波能量的消耗,实现全系统的优化和节能。2. The system and method for desulfurizing and recovering elemental sulfur provided by the invention have the advantages of compact process flow and small occupied area, and can be applied to coal desulfurization before combustion of coal-fired power plants, and utilizing waste heat of coal-fired boiler flue gas to pre-predetermine moisture in raw coal. Removal, reducing the consumption of microwave energy by moisture, achieving system-wide optimization and energy saving.
3、本发明提供的煤炭脱硫并回收单质硫的系统及方法,通过触媒催化高硫煤热解释放的H2S和燃煤烟气中的SO2,省去了传统硫回收工艺中H2S的部分氧化燃烧工序,生成的硫单质经过提纯后可作为副产品出售,具有良好的环境经济效益。3. The system and method for desulfurizing coal and recovering elemental sulfur provided by the invention, and arranging the H 2 S of the high sulfur coal heat by the catalyst to catalyze the release of the SO 2 in the coal combustion flue gas, thereby eliminating the H 2 in the traditional sulfur recovery process. In the partial oxidation combustion process of S, the generated sulfur element can be sold as a by-product after purification, and has good environmental and economic benefits.
4、本发明提供的煤炭脱硫并回收单质硫的系统及方法微波脱硫过程采用红外测温,安装微波泄漏抑制装置,保障系统运行的安全,微波反应器在负压下操作,避免污染物逸散。4. System and method for desulfurizing and recovering elemental sulfur provided by the invention The microwave desulfurization process adopts infrared temperature measurement and installs a microwave leakage suppression device to ensure the safety of the system operation, and the microwave reactor operates under a negative pressure to avoid pollutants from escaping. .
附图说明DRAWINGS
图1为实施例1提供的煤炭脱硫并回收单质硫的系统的结构示意图。1 is a schematic view showing the structure of a system for desulfurizing coal and recovering elemental sulfur provided in Example 1.
其中,1-破碎机;2-烘干器;3-第一引风机;4-红外测温探头;5-微波反应器;6-微波泄漏抑制装置;7-集气罩;8-除尘器;9-换热器;10-硫反应器;11-冷凝器;12-第二引风机;13-烟囱。Among them, 1-crusher; 2-dryer; 3-first induced draft fan; 4-infrared temperature probe; 5-microwave reactor; 6-microwave leakage suppression device; 7-collector cover; 8-dust collector 9-heat exchanger; 10-sulfur reactor; 11-condenser; 12-second induced draft fan; 13-chimney.
另外,图1中的实线表示物料流向,虚线表示气体流向。In addition, the solid line in Fig. 1 indicates the flow direction of the material, and the broken line indicates the flow direction of the gas.
具体实施方式detailed description
下面结合附图并通过具体实施方式来进一步说明本发明的技术方案。The technical solution of the present invention will be further described below with reference to the accompanying drawings and specific embodiments.
实施例1Example 1
一种高硫煤炭脱硫并回收单质硫的系统,如图1所示,所述系统包括:A system for desulfurizing high sulfur coal and recovering elemental sulfur, as shown in Figure 1, the system comprising:
原煤破碎单元,用于破碎原煤,包括破碎机1,所述破碎机1优选为环锤式破碎机1和/或锤式破碎机1;a raw coal crushing unit for crushing raw coal, including a crusher 1, preferably a crusher 1 and/or a hammer crusher 1;
原煤烘干单元,用于烘干原煤,包括烘干器2; Raw coal drying unit for drying raw coal, including dryer 2;
微波脱硫单元,用于煤的微波脱硫,包括微波反应器5,所述微波反应器5内设置有与控制系统相连的红外测温探头4、湿度传感器和压力传感器;所述微波脱硫单元还包括微波泄漏抑制装置6,所述微波泄漏抑制装置6由石墨和/或合金制成,所述微波泄漏抑制装置6设置于微波脱硫单元的底部和/或两侧;a microwave desulfurization unit for microwave desulfurization of coal, comprising a microwave reactor 5, wherein the microwave reactor 5 is provided with an infrared temperature probe 4, a humidity sensor and a pressure sensor connected to the control system; the microwave desulfurization unit further comprises a microwave leakage suppression device 6, which is made of graphite and/or an alloy, and the microwave leakage suppression device 6 is disposed at the bottom and/or both sides of the microwave desulfurization unit;
废气收集单元,用于收集微波脱硫单元产生的含有H2S的气体,包括集气罩7,所述集气罩7顶部设置流量调节阀和气体组分传感器,所述集气罩7为密闭式集气罩或半密闭式集气罩;所述集气罩7与微波反应器5的连接处设置活动侧挡板,侧挡板底部设置有斜气流分布孔;The exhaust gas collecting unit is configured to collect the H 2 S-containing gas generated by the microwave desulfurization unit, and includes a gas collecting cover 7 . The gas collecting cover 7 is provided with a flow regulating valve and a gas component sensor at the top, and the gas collecting cover 7 is sealed. a gas collecting hood or a semi-closed gas collecting hood; a movable side baffle is arranged at a joint of the gas collecting hood 7 and the microwave reactor 5, and a bottom air flow distribution hole is arranged at the bottom of the side baffle;
除尘单元,用于对含有H2S的气体除尘,包括旋风除尘器8、静电除尘器8或布袋式除尘器8中的任意一种或至少两种的组合;a dust removing unit for dedusting a gas containing H 2 S, including any one or a combination of at least two of a cyclone 8, an electrostatic precipitator 8 or a baghouse 8;
单质硫反应单元,用于所述含有H2S的气体与所述含有SO2的燃煤烟气之间的反应,产生单质硫,包括硫反应器10和换热器9,所述硫反应器10中设置催化剂层,所述催化剂层包括经过预处理的Al2O3基触媒催化剂和/或经过预处理的TiO2基触媒催化剂,预处理方法包括氧化还原处理和/或焙烧处理,预处理时间为1-5h,如1.5h、2h、2.5h、3h、3.5h、4h或4.5h等,预处理温度为300-600℃,如320℃、330℃、350℃、380℃、400℃、420℃、450℃、500℃、550℃或580℃等;An elemental sulfur reaction unit for reacting the H 2 S-containing gas with the SO 2 -containing coal-fired flue gas to produce elemental sulfur, including a sulfur reactor 10 and a heat exchanger 9, the sulfur reaction The catalyst layer 10 is provided in the catalyst 10, the catalyst layer comprises a pretreated Al 2 O 3 -based catalyst catalyst and/or a pretreated TiO 2 -based catalyst catalyst, and the pretreatment method comprises a redox treatment and/or a roasting treatment, The treatment time is 1-5h, such as 1.5h, 2h, 2.5h, 3h, 3.5h, 4h or 4.5h, etc., the pretreatment temperature is 300-600 °C, such as 320 °C, 330 °C, 350 °C, 380 °C, 400 °C, 420 ° C, 450 ° C, 500 ° C, 550 ° C or 580 ° C, etc.;
冷凝单元,用于冷凝硫单质硫反应单元产生的高温单质硫,包括冷凝器11,所述冷凝器11为多级冷凝器,如2级冷凝器、3级冷凝器、5级冷凝器或10级冷凝器等,冷凝器管路内设置尖刺螺纹结构;a condensing unit for condensing high-temperature elemental sulfur produced by the sulfur elemental sulfur reaction unit, comprising a condenser 11, the condenser 11 being a multi-stage condenser, such as a 2-stage condenser, a 3-stage condenser, a 5-stage condenser or 10 Stage condenser, etc., a spiked thread structure is arranged in the condenser line;
引风单元,用于将单质硫反应单元中未反应的气体引出,包括第二引风机12;a draft unit for extracting unreacted gas in the elemental sulfur reaction unit, comprising a second induced draft fan 12;
所述燃煤烟气通过第一引风机3引入所述烘干器2中; The coal-fired flue gas is introduced into the dryer 2 through the first induced draft fan 3;
其中,破碎机1、烘干器2和微波反应器5依次相连,集气罩7设置于所述微波反应器5的出气口处,集气罩7的出气口通过除尘器8和换热器9与硫反应器10的进气口相连,燃煤炉的出气口通过烘干器2和换热器9与硫反应器10的进气口相连,冷凝器11的进料口与硫反应器10的出料口相连;第二引风机12设置于硫反应器10和烟囱13之间。The crusher 1, the dryer 2 and the microwave reactor 5 are connected in sequence, and the gas collecting cover 7 is disposed at the gas outlet of the microwave reactor 5, and the gas outlet of the gas collecting cover 7 passes through the dust remover 8 and the heat exchanger. 9 is connected to the inlet of the sulfur reactor 10, and the outlet of the coal-fired furnace is connected to the inlet of the sulfur reactor 10 through the dryer 2 and the heat exchanger 9, and the inlet of the condenser 11 and the sulfur reactor The discharge port of 10 is connected; the second induced draft fan 12 is disposed between the sulfur reactor 10 and the chimney 13.
一种高硫煤脱硫并生产单质硫的工艺流程如下:由储煤仓输送过来的原煤进入破碎机1,将原煤破碎为0.1-50cm的粒径,破碎后的原煤进入烘干器2由热燃煤烟气烘干脱水,使原煤中水分降低至5%以下,烘干后的原煤由连续输送带输送至微波反应器5,在2500-2600MHz,功率300-500W的微波中辐照1-5min,脱硫后的原煤去磨煤机磨粉后喷入锅炉燃烧;A process for desulfurizing high-sulfur coal and producing elemental sulfur is as follows: the raw coal conveyed by the coal storage bin enters the crusher 1, and the raw coal is broken into a particle size of 0.1-50 cm, and the crushed raw coal enters the dryer 2 by heat The coal-fired flue gas is dried and dehydrated to reduce the moisture in the raw coal to less than 5%. The dried raw coal is transported to the microwave reactor 5 by a continuous conveyor belt, and irradiated in a microwave of 2500-2600 MHz and a power of 300-500 W. 5 min, the raw coal after desulfurization is ground to the coal mill for grinding and then injected into the boiler for combustion;
原煤经微波热解生成的含尘、H2S、SO2烟气被集气罩7收集后进入除尘器8,除尘器8将粉尘捕集下来,粉尘捕集效率不低于95%,所捕集下来的除尘灰输送至煤粉仓回用;除尘后的烟气与经烘干器2后的热烟气混合,经过换热器9升温后进入硫反应器10,在触媒的催化作用下生成硫单质蒸气,反应温度在200-400℃,单质硫蒸气经过多级冷凝最后形成硫磺副产品,实现单质硫的高效回收。The dust, H 2 S, SO 2 flue gas generated by the microwave pyrolysis of the raw coal is collected by the gas collecting hood 7 and then enters the dust collector 8 , and the dust collector 8 collects the dust, and the dust collecting efficiency is not less than 95%. The captured dust ash is transported to the pulverized coal bin for reuse; the flue gas after dust removal is mixed with the hot flue gas after the dryer 2, and is heated by the heat exchanger 9 to enter the sulfur reactor 10, and the catalyst is catalyzed by the catalyst. Sulfur elemental vapor is produced under the reaction temperature of 200-400 ° C, and the elemental sulfur vapor is condensed by multiple stages to form a sulfur by-product, thereby achieving efficient recovery of elemental sulfur.
实施例2Example 2
利用实施例1所述系统,采用实施例1的高硫煤脱硫并生产单质硫的方法,进行高硫煤脱硫试验。具体如下:在1000MW燃煤电厂,耗煤量为360t/h,高硫原煤中硫份含量为3.56%,水分含量为6.11%,经过破碎机破碎为20-35cm的粒径,引风机将240℃锅炉烟气引入烘干机前端,烟气中SO2含量为 2000mg/Nm3,O2含量为6%,烟气流量为15×104Nm3/h,烘干后的原煤水分含量降低为4.23%,出口烟气温度降至180℃,烘干后的原煤进入输送带,输送带输送量为50t/h,原煤进入微波反应器,在2540MHz,功率300W的微波中辐照3min,脱硫后煤中硫份降至1.44%,总脱硫效率(本发明如无特殊说明所述总脱硫效率是指硫分前后降低的比值)为59.5%。Using the system described in Example 1, the high sulfur coal desulfurization test was carried out by the method of desulfurizing high sulfur coal of Example 1 and producing elemental sulfur. The details are as follows: in the 1000MW coal-fired power plant, the coal consumption is 360t/h, the sulfur content in the high-sulfur raw coal is 3.56%, the moisture content is 6.11%, and the particle size is 20-35cm after crushing, and the induced draft fan will be 240. °C boiler flue gas is introduced into the front end of the dryer. The SO 2 content in the flue gas is 2000mg/Nm 3 , the O 2 content is 6%, the flue gas flow rate is 15×10 4 Nm 3 /h, and the moisture content of the raw coal after drying is reduced. At 4.23%, the outlet flue gas temperature drops to 180 °C, the raw coal after drying enters the conveyor belt, the conveyor belt conveys 50t/h, the raw coal enters the microwave reactor, and is irradiated for 3min in 2540MHz, 300W microwave, desulfurization The sulfur content in the post coal was reduced to 1.44%, and the total desulfurization efficiency (the total desulfurization efficiency in the present invention is the ratio of the reduction before and after the sulfur content unless otherwise specified) was 59.5%.
微波辐照及原煤输送过程产生的粉尘、H2S等污染物由集气罩收集,集气罩气体流速为8m/s,气体流量为15×104m3/h,O2含量为20%,H2S浓度为708mg/m3,气体温度为120℃,该烟气与锅炉烟气混合经过换热后升温至340℃,在催化剂的作用下发生反应,硫单质转化率为95%,总硫回收率为56.5%,生成硫单质2.85t/h。The dust and H 2 S pollutants generated by microwave irradiation and raw coal transportation are collected by the gas collecting hood. The gas flow rate of the gas collecting hood is 8m/s, the gas flow rate is 15×10 4 m 3 /h, and the O 2 content is 20. %, H2S concentration is 708mg/m 3 , gas temperature is 120 ° C, the flue gas and boiler flue gas are mixed and heat-treated to 340 ° C, reacted under the action of catalyst, sulfur elemental conversion rate is 95%, total The sulfur recovery rate was 56.5%, and the sulfur element was 2.85 t/h.
实施例3Example 3
利用实施例1所述系统,采用实施例1的高硫煤脱硫并生产单质硫的方法,进行高硫煤脱硫试验。具体如下:在500MW燃煤电厂,耗煤量为200t/h,高硫原煤中硫份含量为6.24%,水分含量为7.21%,经过破碎机破碎为15-30cm的粒径,引风机将280℃锅炉烟气引入烘干机前端,烟气中SO2含量为4000mg/Nm3,O2含量为6%,烟气流量为10×104Nm3/h,烘干后的原煤水分含量降低为4.61%,出口烟气温度降至160℃,烘干后的原煤进入输送带,输送带输送量为30t/h,原煤进入微波反应器,在2540MHz,功率500W的微波中辐照5min,脱硫后煤中硫份降至1.52%,总脱硫效率为75.6%。Using the system described in Example 1, the high sulfur coal desulfurization test was carried out by the method of desulfurizing high sulfur coal of Example 1 and producing elemental sulfur. The details are as follows: in the 500MW coal-fired power plant, the coal consumption is 200t/h, the sulfur content in the high-sulfur raw coal is 6.24%, the moisture content is 7.21%, and the crusher is crushed to a particle size of 15-30cm, and the induced draft fan will be 280. °C boiler flue gas is introduced into the front end of the dryer. The SO 2 content in the flue gas is 4000mg/Nm 3 , the O 2 content is 6%, the flue gas flow rate is 10×10 4 Nm 3 /h, and the moisture content of the raw coal after drying is reduced. 4.61%, the outlet flue gas temperature drops to 160 ° C, the raw coal after drying enters the conveyor belt, the conveyor belt transport volume is 30t / h, the raw coal enters the microwave reactor, irradiated in the microwave at 2540MHz, power 500W for 5min, desulfurization The sulfur content in the post coal was reduced to 1.52%, and the total desulfurization efficiency was 75.6%.
微波辐照及原煤输送过程产生的粉尘、H2S等污染物由集气罩收集,集气罩气体流速为10m/s,气体流量为8×104m3/h,O2含量为18%,H2S浓度为17708mg/m3,气体温度为130℃,该烟气与锅炉烟气混合经过换热后升温至 400℃,在催化剂的作用下发生反应,硫单质转化率为96%,总硫回收率为72.6%,生成硫单质3.84t/h。The dust and H 2 S pollutants generated by microwave irradiation and raw coal transportation are collected by the gas collecting hood. The gas flow rate of the gas collecting hood is 10m/s, the gas flow rate is 8×10 4 m 3 /h, and the O 2 content is 18 %, H 2 S concentration is 17708mg / m 3 , gas temperature is 130 ° C, the flue gas and boiler flue gas mixed after heat exchange, the temperature is raised to 400 ° C, the reaction under the action of the catalyst, the sulfur elemental conversion rate is 96% The total sulfur recovery rate was 72.6%, and the sulfur production was 3.84t/h.
实施例4Example 4
利用实施例1所述系统,采用实施例1的高硫煤脱硫并生产单质硫的方法,进行高硫煤脱硫试验。具体如下:在300MW燃煤电厂,耗煤量为150t/h,高硫原煤中硫份含量为3.15%,水分含量为5.12%,经过破碎机破碎为40-50cm的粒径,引风机将260℃锅炉烟气引入烘干机前端,烟气中SO2含量为1500mg/Nm3,O2含量为6%,烟气流量为5×104Nm3/h,烘干后的原煤水分含量降低为2.58%,出口烟气温度降至160℃,烘干后的原煤进入输送带,输送带输送量为30t/h,原煤进入微波反应器,在2500MHz,功率300W的微波中辐照2min,脱硫后煤中硫份降至1.38%,总脱硫效率为56.2%。Using the system described in Example 1, the high sulfur coal desulfurization test was carried out by the method of desulfurizing high sulfur coal of Example 1 and producing elemental sulfur. The details are as follows: in the 300MW coal-fired power plant, the coal consumption is 150t/h, the sulfur content in the high-sulfur raw coal is 3.15%, the moisture content is 5.12%, and the particle size is 40-50cm after crushing, and the induced draft fan will be 260. °C boiler flue gas is introduced into the front end of the dryer. The SO 2 content in the flue gas is 1500mg/Nm 3 , the O 2 content is 6%, the flue gas flow rate is 5×10 4 Nm 3 /h, and the moisture content of the raw coal after drying is reduced. At 2.58%, the outlet flue gas temperature drops to 160 °C, the raw coal after drying enters the conveyor belt, the conveyor belt conveys 30t/h, the raw coal enters the microwave reactor, and is irradiated for 2min in 2500MHz, 300W microwave, desulfurization The sulfur content in the post coal was reduced to 1.38%, and the total desulfurization efficiency was 56.2%.
微波辐照及原煤输送过程产生的粉尘、H2S等污染物由集气罩收集,集气罩气体流速为10m/s,气体流量为5×104m3/h,O2含量为18%,H2S浓度为5312mg/m3,气体温度为140℃,该烟气与锅炉烟气混合经过换热后升温至200℃,在催化剂的作用下发生反应,硫单质转化率为92%,总硫回收率为51.7%,生成硫单质0.69t/h。The dust and H 2 S pollutants generated by microwave irradiation and raw coal transportation are collected by the gas collecting hood. The gas flow rate of the gas collecting hood is 10m/s, the gas flow rate is 5×10 4 m 3 /h, and the O 2 content is 18 %, H 2 S concentration is 5312mg / m 3 , gas temperature is 140 ° C, the flue gas and boiler flue gas mixed heat exchange and then heated to 200 ° C, the reaction under the action of the catalyst, sulfur elemental conversion rate of 92% The total sulfur recovery rate was 51.7%, and the sulfur production was 0.69 t/h.
实施例5Example 5
利用实施例1所述系统,采用实施例1的高硫煤脱硫并生产单质硫的方法,进行高硫煤脱硫试验。具体如下:在600MW燃煤电厂,耗煤量为250t/h,高硫原煤中硫份含量为2.65%,水分含量为5.17%,经过破碎机破碎为10-50mm的粒径,引风机将300℃锅炉烟气引入烘干机前端,烟气中SO2含量为 1000mg/Nm3,O2含量为6%,烟气流量为8×104Nm3/h,烘干后的原煤水分含量降低为2.80%,出口烟气温度降至150℃,烘干后的原煤进入输送带,输送带输送量为30t/h,原煤进入微波反应器,在2600MHz,功率400W的微波中辐照2min,脱硫后煤中硫份降至1.51%,总脱硫效率为43.0%。Using the system described in Example 1, the high sulfur coal desulfurization test was carried out by the method of desulfurizing high sulfur coal of Example 1 and producing elemental sulfur. The details are as follows: in the 600MW coal-fired power plant, the coal consumption is 250t/h, the sulfur content in the high-sulfur raw coal is 2.65%, the moisture content is 5.17%, and the particle size is 10-50mm after crushing, and the induced draft fan will be 300. °C boiler flue gas is introduced into the front end of the dryer. The SO 2 content in the flue gas is 1000mg/Nm 3 , the O 2 content is 6%, the flue gas flow rate is 8×10 4 Nm 3 /h, and the moisture content of the raw coal after drying is reduced. 2.80%, the outlet flue gas temperature drops to 150 ° C, the raw coal after drying enters the conveyor belt, the conveyor belt transport volume is 30t / h, the raw coal enters the microwave reactor, irradiated in the microwave at 2600MHz, power 400W for 2min, desulfurization The sulfur content in the post coal was reduced to 1.51%, and the total desulfurization efficiency was 43.0%.
微波辐照及原煤输送过程产生的粉尘、H2S等污染物由集气罩收集,集气罩气体流速为10m/s,气体流量为5×104m3/h,O2含量为18%,H2S浓度为5666mg/m3,气体温度为120℃,该烟气与锅炉烟气混合经过换热后升温至300℃,在催化剂的作用下发生反应,硫单质转化率为95%,总硫回收率为40.85%,生成硫单质0.76t/h。The dust and H 2 S pollutants generated by microwave irradiation and raw coal transportation are collected by the gas collecting hood. The gas flow rate of the gas collecting hood is 10m/s, the gas flow rate is 5×10 4 m 3 /h, and the O 2 content is 18 %, H 2 S concentration is 5666mg / m 3 , gas temperature is 120 ° C, the flue gas and boiler flue gas mixed after heat exchange, the temperature is raised to 300 ° C, the reaction under the action of the catalyst, the sulfur elemental conversion rate is 95% The total sulfur recovery rate is 40.85%, and the sulfur production is 0.76t/h.
实施例2-5中的催化剂选自经过预处理的Al2O3基触媒催化剂,所述预处理为焙烧处理,焙烧时间为3h,焙烧温度为500℃。The catalysts of Examples 2-5 were selected from the pretreated Al 2 O 3 -based catalysts, which were calcined at a calcination time of 3 h and a calcination temperature of 500 °C.
实施例2-5中的催化剂还可选自上述催化剂之外的经过预处理的Al2O3基触媒催化剂和/或经过预处理的TiO2基触媒催化剂,预处理方法包括氧化还原处理和/或焙烧处理,预处理时间为1-5h,如1.5h、2h、2.5h、3.5h、4h或4.5h等,预处理的温度为300-600℃,如320℃、330℃、350℃、380℃、400℃、420℃、450℃、550℃或580℃等。The catalyst of Examples 2-5 may also be selected from a pretreated Al 2 O 3 -based catalyst catalyst and/or a pretreated TiO 2 -based catalyst catalyst other than the above catalysts, the pretreatment method including redox treatment and/or Or roasting treatment, the pretreatment time is 1-5h, such as 1.5h, 2h, 2.5h, 3.5h, 4h or 4.5h, etc., the pretreatment temperature is 300-600 ° C, such as 320 ° C, 330 ° C, 350 ° C, 380 ° C, 400 ° C, 420 ° C, 450 ° C, 550 ° C or 580 ° C and so on.
申请人声明,以上所述仅为本发明的具体实施方式,但本发明的保护范围并不局限于此,所属技术领域的技术人员应该明了,任何属于本技术领域的技术人员在本发明揭露的技术范围内,可轻易想到的变化或替换,均落在本发明的保护范围和公开范围之内。 The Applicant claims that the above description is only the specific embodiment of the present invention, but the scope of the present invention is not limited thereto, and those skilled in the art should understand that any person skilled in the art disclosed in the present invention Variations or substitutions that are conceivable within the scope of the invention are within the scope of the invention and the scope of the disclosure.

Claims (12)

  1. 一种煤炭脱硫并回收单质硫的系统,包括微波脱硫单元,其特征在于,所述煤炭脱硫并回收单质硫的系统还包括:A system for desulfurizing coal and recovering elemental sulfur, comprising a microwave desulfurization unit, wherein the system for desulfurizing and recovering elemental sulfur of the coal further comprises:
    原煤烘干单元,用于含有SO2的燃煤烟气对煤炭的烘干,得到干燥的煤炭并排出换热后的燃煤烟气;The raw coal drying unit is used for drying the coal by the coal-fired flue gas containing SO 2 , obtaining the dried coal and discharging the coal-fired flue gas after the heat exchange;
    废气收集单元,用于收集微波脱硫单元产生的含有H2S的气体;An exhaust gas collecting unit for collecting the H 2 S-containing gas generated by the microwave desulfurization unit;
    单质硫反应单元,用于所述含有H2S的气体与所述换热后的燃煤烟气之间的反应,产生单质硫;An elemental sulfur reaction unit for reacting between the H 2 S-containing gas and the heat-exchanged coal-fired flue gas to produce elemental sulfur;
    其中,所述原煤烘干单元的出料口与微波脱硫单元的进料口相连,所述废气收集单元设置于所述微波脱硫单元的出气口处,单质硫反应单元的进气口分别与原煤烘干单元的出气口和废气收集单元的出气口相连。Wherein, the discharge port of the raw coal drying unit is connected to the feed port of the microwave desulfurization unit, the exhaust gas collection unit is disposed at the air outlet of the microwave desulfurization unit, and the air inlet of the elemental sulfur reaction unit is respectively separated from the raw coal The air outlet of the drying unit is connected to the air outlet of the exhaust gas collection unit.
  2. 根据权利要求1所述的煤炭脱硫并回收单质硫的系统,其特征在于,所述系统还包括原煤破碎单元,所述原煤破碎单元与原煤烘干单元的进料口相连,或所述原煤烘干单元通过原煤破碎单元与微波脱硫单元相连。The system for desulfurizing and recovering elemental sulfur according to claim 1, wherein the system further comprises a raw coal crushing unit, the raw coal crushing unit is connected to a feed port of the raw coal drying unit, or the raw coal is baked. The dry unit is connected to the microwave desulfurization unit through a raw coal crushing unit.
  3. 根据权利要求2所述的煤炭脱硫并回收单质硫的系统,其特征在于,所述原煤破碎单元包括破碎机,所述破碎机优选为环锤式破碎机和/或锤式破碎机。The system for desulfurizing and recovering elemental sulfur according to claim 2, wherein the raw coal crushing unit comprises a crusher, and the crusher is preferably a ring hammer crusher and/or a hammer crusher.
  4. 根据权利要求1所述的煤炭脱硫并回收单质硫的系统,其特征在于,所述原煤烘干单元包括烘干器;The system for desulfurizing and recovering elemental sulfur in coal according to claim 1, wherein the raw coal drying unit comprises a dryer;
    优选地,所述微波反应单元包括微波反应器,所述微波反应器内设置有与集中控制系统分别相连的红外测温探头、湿度传感器和压力传感器;Preferably, the microwave reaction unit comprises a microwave reactor, wherein the microwave reactor is provided with an infrared temperature probe, a humidity sensor and a pressure sensor respectively connected to the centralized control system;
    优选地,所述微波脱硫单元还包括微波泄漏抑制装置,所述微波泄漏抑制装置设置于微波脱硫单元的底部和/或两侧;Preferably, the microwave desulfurization unit further includes a microwave leakage suppression device disposed at a bottom and/or both sides of the microwave desulfurization unit;
    优选地,所述微波泄漏抑制装置由石墨和/或合金制成。 Preferably, the microwave leakage suppression device is made of graphite and/or an alloy.
  5. 根据权利要求1或2所述的煤炭脱硫并回收单质硫的系统,其特征在于,所述系统还包括除尘单元,所述废气收集单元的出气口通过所述除尘单元与单质硫反应单元的进气口相连;The system for desulfurizing and recovering elemental sulfur in coal according to claim 1 or 2, wherein the system further comprises a dust removing unit, and an air outlet of the exhaust gas collecting unit passes through the dust removing unit and the elemental sulfur reaction unit. Air port connection;
    优选地,所述除尘单元包括旋风除尘器、静电除尘器或布袋式除尘器中的任意一种或至少两种的组合。Preferably, the dust removing unit comprises any one or a combination of at least two of a cyclone, an electrostatic precipitator or a bag filter.
  6. 根据权利要求1-5之一所述的煤炭脱硫并回收单质硫的系统,其特征在于,所述废气收集单元包括集气罩,所述集气罩顶部设置流量调节阀和气体组分传感器;The system for desulfurizing and recovering elemental sulfur according to any one of claims 1 to 5, wherein the exhaust gas collecting unit comprises a gas collecting hood, and a flow regulating valve and a gas component sensor are disposed at the top of the gas collecting hood;
    优选地,所述集气罩为密闭式集气罩或半密闭式集气罩,所述集气罩与微波脱硫单元的连接处设置活动侧挡板,侧挡板底部设置有斜气流分布孔;Preferably, the gas collecting hood is a closed gas collecting hood or a semi-closed gas collecting hood, a movable side baffle is arranged at a joint of the gas collecting hood and the microwave desulfurization unit, and a diagonal air flow distribution hole is arranged at the bottom of the side baffle ;
    优选地,所述单质硫反应单元包括硫反应器,所述硫反应器中设置催化剂层,所述催化剂层包括经过预处理的Al2O3基触媒催化剂和/或经过预处理的TiO2基触媒催化剂,预处理方法包括氧化还原处理和/或焙烧处理,预处理时间为1-5h,预处理温度为300-600℃;Preferably, the elemental sulfur reaction unit comprises a sulfur reactor, in which a catalyst layer is provided, the catalyst layer comprising a pretreated Al 2 O 3 -based catalyst catalyst and/or a pretreated TiO 2 group Catalyst catalyst, the pretreatment method comprises redox treatment and/or roasting treatment, the pretreatment time is 1-5 h, and the pretreatment temperature is 300-600 ° C;
    优选地,所述单质硫反应单元还包括预热装置,所述废气收集单元的出气口和原煤烘干单元的出气口通过所述预热装置与硫反应器的进气口相连;Preferably, the elemental sulfur reaction unit further comprises a preheating device, and an air outlet of the exhaust gas collecting unit and an air outlet of the raw coal drying unit are connected to an air inlet of the sulfur reactor through the preheating device;
    优选地,所述预热装置包括换热器。Preferably, the preheating device comprises a heat exchanger.
  7. 根据权利要求1-6之一所述的煤炭脱硫并回收单质硫的系统,其特征在于,所述系统还包括冷凝单元,所述冷凝单元的进料口与单质硫反应单元的出料口相连;A system for desulfurizing and recovering elemental sulfur in coal according to any one of claims 1 to 6, characterized in that the system further comprises a condensing unit, the feed port of the condensing unit being connected to the discharge port of the elemental sulfur reaction unit ;
    优选地,所述冷凝单元包括多级冷凝器,冷凝器管路内设置尖刺螺纹;Preferably, the condensing unit comprises a multi-stage condenser, and a spiking thread is arranged in the condenser line;
    优选地,所述系统还包括引风单元,所述引风单元连接于所述单质硫反应单元的出气口处; Preferably, the system further includes a draft unit connected to an air outlet of the elemental sulfur reaction unit;
    优选地,所述引风单元包括第二引风机。Preferably, the air guiding unit comprises a second induced draft fan.
  8. 一种利用权利要求1-7之一所述的煤炭脱硫并回收单质硫的系统进行煤炭脱硫并回收单质硫的方法,其特征在于,所述方法包括如下步骤:A method for desulfurizing coal and recovering elemental sulfur by using the system for desulfurizing coal and recovering elemental sulfur according to any one of claims 1-7, wherein the method comprises the following steps:
    (1)采用含有SO2的燃煤烟气将原煤烘干,得到干燥的原煤和换热后的燃煤烟气;干燥的原煤进行微波脱硫,得到含有H2S的气体;(1) drying the raw coal with coal-fired flue gas containing SO 2 to obtain dried raw coal and coal-fired flue gas after heat exchange; the dried raw coal is subjected to microwave desulfurization to obtain a gas containing H 2 S;
    (2)含有H2S的气体与换热后的燃煤烟气进行反应,生成单质硫。(2) The gas containing H 2 S reacts with the coal-fired flue gas after heat exchange to form elemental sulfur.
  9. 根据权利要求8所述的方法,其特征在于,步骤(1)所述原煤经破碎后再进行烘干或烘干后先破碎再进行微波脱硫;The method according to claim 8, wherein the raw coal in the step (1) is crushed, dried or dried, and then first broken and then subjected to microwave desulfurization;
    优选地,破碎后的原煤的粒径为0.1-50cm;Preferably, the crushed raw coal has a particle size of 0.1-50 cm;
    优选地,步骤(1)所述干燥的原煤中水的质量百分含量为5%以下;Preferably, the mass percentage of water in the dried raw coal in step (1) is 5% or less;
    优选地,步骤(1)所述微波脱硫使用的微波频率为2500-2600MHz,微波功率为300-500W,微波脱硫时间为1-5min。Preferably, the microwave desulfurization used in the step (1) uses a microwave frequency of 2500-2600 MHz, a microwave power of 300-500 W, and a microwave desulfurization time of 1-5 min.
  10. 根据权利要求8或9所述的方法,其特征在于,步骤(2)所述含有H2S的气体先除尘再与换热后的燃煤烟气进行反应;The method according to claim 8 or 9, wherein the gas containing H 2 S in the step (2) is first dedusted and then reacted with the coal-fired flue gas after the heat exchange;
    优选地,所述除尘效率不低于95%。Preferably, the dust removal efficiency is not less than 95%.
  11. 根据权利要求8-10之一所述的方法,其特征在于,步骤(2)所述反应的温度为200-400℃;The method according to any one of claims 8 to 10, wherein the temperature of the reaction in the step (2) is 200-400 ° C;
    优选地,步骤(2)所述反应在经过预处理的Al2O3基触媒催化剂和/或经过预处理的TiO2基触媒催化剂的催化下进行,预处理方法包括氧化还原处理和/或焙烧处理,预处理时间为1-5h,预处理的温度为300-600℃。Preferably, the reaction in the step (2) is carried out under the catalysis of a pretreated Al 2 O 3 -based catalyst and/or a pretreated TiO 2 -based catalyst, and the pretreatment method comprises redox treatment and/or calcination. Treatment, pretreatment time is 1-5h, pretreatment temperature is 300-600 °C.
  12. 根据权利要求8-11之一所述的方法,其特征在于,所述方法包括如下步骤:Method according to one of the claims 8-11, characterized in that the method comprises the following steps:
    (1)将原煤破碎至0.1-50cm后,利用含有SO2的燃煤烟气与破碎后的原 煤换热,得到水的质量百分含量为5%以下的干燥原煤和换热后的燃煤烟气;干燥原煤进行微波脱硫,微波的频率为2500-2600MHz,微波功率为300-500W,微波脱硫时间为1-5min,得到含有H2S的气体;(1) After the raw coal is crushed to 0.1-50cm, the coal-fired flue gas containing SO 2 is exchanged with the recovered raw coal to obtain dry raw coal with a water content of 5% or less and coal after heat exchange. Flue gas; dry raw coal for microwave desulfurization, microwave frequency is 2500-2600MHz, microwave power is 300-500W, microwave desulfurization time is 1-5min, and gas containing H 2 S is obtained;
    (2)换热后的燃煤烟气与含有H2S的气体在200-400℃条件下进行催化反应,催化剂为经过预处理的Al2O3基触媒催化剂和/或经过预处理的TiO2基触媒催化剂,预处理方法包括氧化还原处理和/或焙烧处理,预处理时间为1-5h,预处理温度为300-600℃,得到单质硫产品。 (2) The coal-fired flue gas after heat exchange and the gas containing H 2 S are catalytically reacted at 200-400 ° C. The catalyst is a pretreated Al 2 O 3 -based catalyst and/or pretreated TiO 2 based catalyst catalyst, redox treatment comprising a pretreatment and / or calcination treatment, pretreatment time is 1-5h, pretreatment temperature of 300-600 deg.] C, to give elemental sulfur product.
PCT/CN2017/100690 2017-06-07 2017-09-06 System and method for desulfurizing coal and recovering elemental sulfur WO2018223546A1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CN201710424225.3 2017-06-07
CN201710424225.3A CN107150998B (en) 2017-06-07 2017-06-07 System and method for coal desulfurization and elemental sulfur recovery

Publications (1)

Publication Number Publication Date
WO2018223546A1 true WO2018223546A1 (en) 2018-12-13

Family

ID=59795824

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/CN2017/100690 WO2018223546A1 (en) 2017-06-07 2017-09-06 System and method for desulfurizing coal and recovering elemental sulfur

Country Status (2)

Country Link
CN (1) CN107150998B (en)
WO (1) WO2018223546A1 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109554537B (en) * 2018-11-19 2020-05-05 北京汉唐环保科技股份有限公司 Special desulfurization equipment for iron ore
CN110669561B (en) * 2019-10-28 2020-08-04 安徽理工大学 Heat energy recovery processing device for coal desulfurization
CN110655964B (en) * 2019-10-28 2020-08-04 安徽理工大学 Treatment device and method applied to microwave desulfurization of coal
TWI769887B (en) * 2021-07-09 2022-07-01 永虹先進材料股份有限公司 Coal water removal equipment

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101250458A (en) * 2008-04-03 2008-08-27 南京大学 Method for coal desulfurization catalyzed by microwave
US20110044872A1 (en) * 2008-01-21 2011-02-24 Mitsubishi Heavy Industries, Ltd. Flue gas control system of coal combustion boiler and operating method thereof
CN103409198A (en) * 2013-07-23 2013-11-27 山东天力干燥股份有限公司 Drying, desulphurization and dehydration system and process for low-rank coal or coal slime
CN104001403A (en) * 2014-05-06 2014-08-27 中国科学院过程工程研究所 Active coke/charcoal flue gas desulphurization denitration and elemental sulfur-recovery technology and device
CN205669015U (en) * 2015-08-25 2016-11-02 张相平 A kind of coupled system of sulphur coal desulfurization before combustion

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0841467A (en) * 1994-07-27 1996-02-13 Hitachi Ltd Method for purifying produced gas in coal gasifying plant
CN102816623B (en) * 2012-08-14 2014-03-19 南京三乐电子信息产业集团有限公司 Coal quality improvement apparatus for microwave low temperature dehydration and desulfurization
CN203333613U (en) * 2013-07-23 2013-12-11 山东天力干燥股份有限公司 Low-rank coal or coal slime drying, dehydration and desulfurization system
CN203890315U (en) * 2014-04-21 2014-10-22 中国矿业大学 Device for separating and collecting sulfur-containing gas in microwave joint aid coal desulfurization
CN204039062U (en) * 2014-08-06 2014-12-24 山东神华山大能源环境有限公司 A kind of preparation facilities of flue gas desulfurization activated coke
CN104327900A (en) * 2014-11-19 2015-02-04 中国科学院上海高等研究院 Direct desulfurization method of high-sulfur coal by microwave radiation

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20110044872A1 (en) * 2008-01-21 2011-02-24 Mitsubishi Heavy Industries, Ltd. Flue gas control system of coal combustion boiler and operating method thereof
CN101250458A (en) * 2008-04-03 2008-08-27 南京大学 Method for coal desulfurization catalyzed by microwave
CN103409198A (en) * 2013-07-23 2013-11-27 山东天力干燥股份有限公司 Drying, desulphurization and dehydration system and process for low-rank coal or coal slime
CN104001403A (en) * 2014-05-06 2014-08-27 中国科学院过程工程研究所 Active coke/charcoal flue gas desulphurization denitration and elemental sulfur-recovery technology and device
CN205669015U (en) * 2015-08-25 2016-11-02 张相平 A kind of coupled system of sulphur coal desulfurization before combustion

Also Published As

Publication number Publication date
CN107150998B (en) 2020-01-07
CN107150998A (en) 2017-09-12

Similar Documents

Publication Publication Date Title
WO2018223546A1 (en) System and method for desulfurizing coal and recovering elemental sulfur
CN102303883B (en) Method for preparing calcium oxide and sulfur by double-atmosphere fluidized roasting of desulfurated gypsum
CN105214478A (en) The integral process of a kind of coke oven flue exhuast gas desulfurization denitration and waste heat recovery
CN102502527B (en) Method for joint production of sulfuric acid and refined iron powder by mixed burning of ferrous sulfate and pyrite
CN108190843B (en) Entrained flow bed and method for recovering sulfur by reducing SO 2 in desulfurization and decomposition gas with carbon-based material
CN101513993A (en) Method using magnesium sulphate to produce sulphuric acid
CN102730997A (en) Method and installation for producing cement clinker
CN109987587A (en) A kind of sulfuric acid Preparation equipment and technique
CN109775666B (en) Device and method for preparing sulfur by coal gasification in cooperation with calcium sulfate calcination and carbon thermal reduction
CN108397777B (en) A kind of domestic garbage gasification electricity generation system
CN110304631A (en) A kind of activated coke post forming device and technique
CN213943158U (en) Typical sewage treatment waste activated carbon regeneration treatment system
CN109453591A (en) A kind of carbon black waste gas treatment process
CN108083279A (en) The system and method for handling carbide slag
US11292718B2 (en) Process for preparing sulfur from reduction of sulfate/ nitrate by iron-carbon and recovering desulfurization/ denitration agents
CN207552243U (en) A kind of system of domestic garbage resource
CN105238472A (en) Method for producing clean coal by utilizing industrial waste heat
CN103822439B (en) One utilizes surplus heat of power plant to carry out pre-dried system and method to brown coal
CN106824094B (en) It is a kind of to remove power-plant flue gas CO using modified gangue2System and its implementation method
CN105042610A (en) CFB oxygen-enriched combustion smoke near zero emission power generation system
CN108529844A (en) A kind of sewage sludge gas heat carrier classification low temperature pyrogenation system and method
CN110683520B (en) Process for preparing sulfuric acid by regenerating low-concentration dilute waste sulfuric acid
CN110015686A (en) Titanium slag recycles the method for titanium dioxide and the method from denitrating catalyst recycling tungsten, titanium and vanadium
CN215049582U (en) Sludge shock wave pyrolysis, drying and mineralization treatment system
CN204039334U (en) Coal gas circulation coal wholegrain radial sector pyrolysis coupling Active coke preparation system

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 17912906

Country of ref document: EP

Kind code of ref document: A1

NENP Non-entry into the national phase

Ref country code: DE

122 Ep: pct application non-entry in european phase

Ref document number: 17912906

Country of ref document: EP

Kind code of ref document: A1