CN206384875U - A kind of low-temp low-pressure desulfurization wastewater evaporating - Google Patents

A kind of low-temp low-pressure desulfurization wastewater evaporating Download PDF

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Publication number
CN206384875U
CN206384875U CN201621383340.8U CN201621383340U CN206384875U CN 206384875 U CN206384875 U CN 206384875U CN 201621383340 U CN201621383340 U CN 201621383340U CN 206384875 U CN206384875 U CN 206384875U
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road
evaporator
connects
pump
condenser
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赵莉
李琳
刘宇
吴洋文
董长青
陆强
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North China Electric Power University
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North China Electric Power University
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Abstract

The utility model is related to a kind of low-temp low-pressure desulfurization wastewater evaporating, and the device includes flue gas processing system and evaporation and crystallization system;Wherein in evaporation and crystallization system, heated up using flue gas after deduster for recycling waste water, include high pressure atomizing nozzle and gas washer in evaporator, the waste water and cleaning steam being respectively used to after atomization heating, produce and wastewater supernatant fluid condensation is utilized after steam, the mud of evaporation and concentration sprays into air preheater rear pass, is evaporated crystallization and is removed by deduster.Device of the present utility model can be used for the purified treatment of power plant desulfurization wastewater and similar sewage disposal.Involved flash conditions are low temperature, corrosion of the waste water to vapo(u)rization system is greatly reduced, equipment scaling slagging is effectively prevented, energy utilization rate is improved using flue gas processing system, final product has reached salt, water separation, realizes desulfurization wastewater zero-emission.

Description

A kind of low-temp low-pressure desulfurization wastewater evaporating
Technical field
The utility model belongs to technical field of water pollution control, and in particular to a kind of low-temp low-pressure desulfurization wastewater evaporation process Device.
Background technology
Limestone-gypsum method flue gas desulfurization technology is the desulfurizing industrial fume technology being most widely used at present, the process The desulfurization wastewater of generation is most intractable to turn into power plant the characteristics of its salt content is high, water quality is in acid and heavy metal severe overweight Waste water.Conventional desulfuration waste water treatment process mainly includes neutralizing, flocculates, precipitates and outer row at present;But its plant area face Product is big, investment is high, and technological process is complicated, and the desulfurization wastewater after often handling is not still up to standard.And the desulfurization developed in recent years is given up Water new technology, such as film process, flue spraying, MED (multiple-effect evaporation crystallization processes), although the recycling to waste water rises necessarily Effect, but problem is still more, and it is serious that phenomenon is blocked up in such as dirt of film process, need to frequently change filter membrane;Flue spraying treatment amount is small, holds Corrosion easily is produced to flue and deduster;The problems such as MED evaporation treatment process then has easy fouling, consumes energy high.
With running down for water resource, the pay attention to day by day of Environmental protection, " zero-emission " turns into the target chased. Waste water zero emission is defined as industrial and mining enterprises not to any waste water of environmental emission, industrial wastewater fully recovering.And power plant will realize " zero-emission ", main difficult point is then the processing of desulfurization wastewater.The features such as desulfurization wastewater has high salinity, high rigidity, " zero-emission Put " difficulty is high, include at this stage the problem of power plant desulfurization wastewater " zero-emission " technique urgent need to resolve it is following some:
(1) how the solid water in waste water to be separated, directly obtains the water of recoverable.
(2) such as how less energy resource consumption handles waste water, reduces operating cost.
(3) how equipment scaling is reduced, it is ensured that the cycle of operation of equipment and safety.
Utility model content
The purpose of this utility model is to provide a kind of low-temp low-pressure desulfurization wastewater evaporating, to reduce processing procedure Energy resource consumption so that reduce processing desulfurization wastewater operating cost, realize the quick processing of desulfurization wastewater.
To achieve the above object, the technical solution adopted in the utility model is:
The flue gas processing system includes air preheater, deduster and desulfurizing tower.
The evaporation and crystallization system includes evaporator, sludge pump one, heater, high pressure atomizing nozzle, gas washer, vacuum Pump, condenser, draining pump, residue extraction mechanism, sludge pump two, water storage apparatus, feed pump and atomizer, wherein gas washer include removing Mist plate, sieve plate pipeline, sieve plate, supply line and flushing line.
Water storage apparatus supernatant outlet in the evaporation and crystallization system connects entrance of water-supplying pump by the road;The feed pump Outlet connects condenser tube-side inlet by the road;The condenser tube side outlet connects evaporator tank body by the road;The evaporation Device tank body connects the entrance of sludge pump one by the road;The sludge pump one exports connection heater tube-side inlet by the road;It is described to add Hot device tube side outlet connects high pressure atomizing nozzle by the road;The heater shell side inlet connects deduster rear pass point by the road Branch;The heater shell-side outlet connects deduster rear pass branch by the road;The high pressure atomizing nozzle is placed in evaporator tank Internal portion;The gas washer main body connects evaporator tank body through flange;The gas washer steam (vapor) outlet connects condenser by the road Shell side inlet;The condenser shell-side outlet connects draining pump intake by the road;The vavuum pump bleeding point connects cold by the road Condenser incoagulable gas outlet;The evaporator deslagging outlet connects residue extraction mechanism entrance by the road;The residue extraction mechanism goes out Mouth connects the entrance of sludge pump two by the road;The sludge pump two is exported connects atomizer by the road;The atomizer arrangement Inside air preheater rear pass.
Preferably, be spaced apart successively from the bottom to top inside gas washer in the evaporation and crystallization system four pieces of sieve plates and One block of demisting plate;Wherein sieve plate pipeline is fixed on sieve plate.
Preferably, the water storage apparatus in the evaporation and crystallization system is water tank.
At the same time, to achieve the above object, the utility model provides a kind of low-temp low-pressure desulfurization wastewater evaporation process Technique, comprises the following steps:
1) deduster dedusting is entered after flue gas reclaims used heat through air preheater, the flue gas after dedusting is de- into desulfurizing tower Sulphur, produces desulfurization wastewater;
2) the desulfurization wastewater stoste for producing desulfurizing tower injects water storage apparatus, after settlement, takes on the waste water of water storage apparatus Clear liquid injects condenser tube side through feed pump, and low pressure evaporator is injected after steam preheating in condenser tube side, and with evaporation The desulfurization wastewater with certain temperature is mixed in device;Waste water is extracted out through sludge pump one after mixing turns into highly pressurised liquid, enters back into and adds The heating of hot device tube side, waste water heating institute calorific requirement comes from fume afterheat after deduster wherein at this, flue gas walk heater shell side with Waste water in tube side is through row heat exchange;Waste water after heating sprays through high pressure atomizing nozzle to be formed hot waste water droplet and is again introduced into Flashed in low pressure evaporator, form steam and the drop of non-evaporating completely;The drop of non-evaporating completely then drops back into evaporator On liquid level, and steam then removes tiny salt by sieve plate plate hole layer by layer, gas washing water and demisting plate from the bottom to top through gas washer Grain and droplet, form clean steam, then enter condenser shell side through gas washer steam (vapor) outlet, and wherein gas washing water is from top to bottom passed through Sieve plate pipeline is flowed into evaporator, and wherein flushing line is periodically turned on, and supply line is persistently opened;The condensed device shell of clean steam Journey, with condenser tube side wastewater supernatant fluid heat-shift, condensation forms condensed water, then is discharged by draining pump for power plant's reuse, And incoagulable gas is then drained to maintain the vacuum of whole evaporation and crystallization system by vacuum pumped in condenser;Work as evaporator When interior sludge concentration reaches setting value, stop being evaporated in vacuo, base of evaporator sludge is discharged by residue extraction mechanism, taken out through sludge pump two Go out, the flue sprayed into by atomizer behind air preheater is evaporated, and forms steam and salt particle, and steam is discharged with flue gas, salt Particle is then removed by deduster.
Preferably, the step 2) in after deduster the temperature range of flue gas meet 100~150 DEG C, connect heater The deduster rear pass branch of shell-side outlet pipeline is located at after the deduster rear pass branch of connection heater shell side entrance pipe 2~the 4m in face.
Preferably, the step 2) in the heat transfer type of flue gas in heater and waste water be countercurrent heat-transfer;Condenser In wastewater supernatant fluid and steam heat transfer type be countercurrent heat-transfer, heater shell side smear teflon coating.
Preferably, the step 2) in the temperature range of evaporator meet 45-55 DEG C, vacuum pressure range is met 0.0095-0.0158MPa。
Preferably, the step 2) in evaporator the overall density of waste water maintain 45-55%.
Preferably, the step 2) on gas washer sieve plate gas washing water be that saturation clear water and thickness at 45-55 DEG C is 1-4mm。
Preferably, the step 2) in gas washer sieve plate length of pipe be gas washer total height 1/6th (1/ 6)。
The beneficial effects of the utility model are:
1) evaporated using low-temperature condition, reduce corrosivity of the waste water to equipment, it is to avoid equipment scaling, while to utilize Low-temperature heat source provides facility;Evaporator tank body is slack tank body, and internal gas washer uses layered arrangement, and layer is carried out to the steam of extraction Layer washing, can control condensed water water quality, to realize the up to standard of water quality by adjusting suction pressure.
2) use flue gas after deduster to provide energy for waste water evaporation, make use of low temperature exhaust heat, removed while avoiding and utilizing Situation of the dust to heater serious wear after flue gas before dirt device;Heater shell side smears polytetrafluoroethylene (PTFE), prevents flue gas corrosion Heater;Steam condenser heat heated waste water is utilized in condenser, capacity usage ratio is improved.
3) it is evaporated using by highly enriched desulfurization wastewater penetrating flue, reduces flue waste water evaporation capacity, it is to avoid useless Corrosion of the water evaporation not exclusively to flue and deduster, while realizing that salt solution is separated, reaches desulfurization wastewater zero-emission.
Brief description of the drawings
The structural representation for the low-temp low-pressure desulfurization wastewater evaporating that Fig. 1 provides for the utility model;
Wherein, 11, air preheater;12nd, deduster;13rd, desulfurizing tower;20th, evaporator;21st, sludge pump one;22nd, heat Device;23rd, high pressure atomizing nozzle;24th, gas washer;25th, vavuum pump;26th, condenser;27th, draining pump;28th, residue extraction mechanism;29th, it is dirty Dredge pump two;30 water storage apparatus;31st, feed pump;32nd, atomizer.
The structural representation inside gas washer 24 that Fig. 2 provides for the utility model;
Wherein, 41, demisting plate;42nd, sieve plate pipeline;43rd, sieve plate;44th, supply line;45th, flushing line.
Embodiment
Embodiment 1:
Reference picture 1, the low-temp low-pressure desulfurization wastewater evaporating described in the present embodiment, device includes flue gas Processing system 1 and evaporation and crystallization system 2.
The flue gas processing system 1 includes air preheater 11, deduster 12 and desulfurizing tower 13.
The evaporation and crystallization system 2 includes evaporator 20, sludge pump 1, heater 22, high pressure atomizing nozzle 23, gas washing Device 24, vavuum pump 25, condenser 26, draining pump 27, residue extraction mechanism 28, sludge pump 2 29, water storage apparatus 30, feed pump 31 and mist Change nozzle 32, wherein gas washer (such as Fig. 2) 24 includes demisting plate 41, sieve plate pipeline 42, sieve plate 43, supply line 44 and flush pipe Road 45.
The supernatant outlet of water storage apparatus 30 in the evaporation and crystallization system 2 connects the entrance of feed pump 31 by the road;It is described Feed pump 31 exports the connection tube-side inlet of condenser 26 by the road;The tube side of condenser 26 outlet connects evaporator 20 by the road Tank body;The tank body of evaporator 20 connects the entrance of sludge pump 1 by the road;The outlet of sludge pump 1 connection by the road adds The hot tube-side inlet of device 22;The tube side of heater 22 outlet connects high pressure atomizing nozzle 23 by the road;The shell side of heater 22 Entrance connects the rear pass branch of deduster 12 by the road;The shell-side outlet of heater 22 connects the rear pass of deduster 12 by the road Branch;The high pressure atomizing nozzle 23 is placed in the tank interior of evaporator 20;The main body of gas washer 24 connects evaporator through flange 20 tank bodies;The steam (vapor) outlet of gas washer 24 connects the shell side inlet of condenser 26 by the road;The shell-side outlet of condenser 26 warp Pipeline connects the entrance of draining pump 27;The bleeding point of vavuum pump 25 connects the incoagulable gas outlet of condenser 26 by the road;Institute State the outlet of the deslagging of evaporator 20 and connect the entrance of residue extraction mechanism 28 by the road;The residue extraction mechanism 28 is exported connects sludge pump by the road 2 29 entrances;The outlet of sludge pump 2 29 connects atomizer 32 by the road;The atomizer 32 is arranged in air preheat Inside the rear pass of device 11.
It is spaced apart four pieces of sieve plates 43 and one piece inside gas washer 24 in the evaporation and crystallization system 2 successively from the bottom to top Demisting plate 41;Wherein sieve plate pipeline 42 is fixed on sieve plate 43.
Water storage apparatus 30 in the evaporation and crystallization system 2 is water tank.
Low-temp low-pressure desulfurization wastewater evaporation technology described in the present embodiment, is comprised the following steps that:
1) dedusting of deduster 12 is entered after flue gas reclaims used heat through air preheater 11, the flue gas after dedusting enters desulfurizing tower Desulfurization 13, produces desulfurization wastewater;
2) the desulfurization wastewater stoste for producing desulfurizing tower 13 injects water storage apparatus 30, after settlement, takes water storage apparatus 30 Wastewater supernatant fluid injects the tube side of condenser 26 through feed pump 31, and low pressure evaporation is injected after steam is preheated in the tube side of condenser 26 Device 20, and mixed with the desulfurization wastewater with certain temperature in evaporator 20;Waste water is extracted out through sludge pump 1 and turned into after mixing Highly pressurised liquid, enters back into the heating of the tube side of heater 22, and waste water heating institute calorific requirement is come from after deduster 12 more than flue gas wherein at this Heat, flue gas walks the shell side of heater 22 with the waste water in tube side through row heat exchange;Waste water after heating sprays through high pressure atomizing nozzle 23 Go out to be formed hot waste water droplet and be again introduced into low pressure evaporator 20 to be flashed, the drop of formation steam and non-evaporating completely; The drop of non-evaporating completely is then dropped back on evaporator liquid level, and steam is then through gas washer 24 from the bottom to top by the plate of sieve plate 43 layer by layer Hole, gas washing water and demisting plate 41 remove tiny salt particle and droplet, clean steam are formed, then through the steam (vapor) outlet of gas washer 24 Into the shell side of condenser 26, wherein gas washing water is flowed into evaporator 20 through sieve plate pipeline 42 under upper, wherein flushing line 45 Periodically turn on, supply line 44 is persistently opened;The condensed shell side of device 26 of clean steam, the wastewater supernatant fluid with the tube side of condenser 26 Heat-shift, condensation forms condensed water, then is discharged by draining pump 27 for power plant's reuse, and incoagulable gas is then in condenser 26 Extracted out and drained to maintain the vacuum of whole evaporation and crystallization system by vavuum pump 25;When sludge concentration reaches setting in evaporator 20 During value, stop being evaporated in vacuo, the base sludge of evaporator 20 is discharged by residue extraction mechanism 28, extracted out through sludge pump 2 29, sprayed by atomization The flue evaporation that mouth 32 is sprayed into behind air preheater 11, forms steam and salt particle, steam is discharged with flue gas, salt particle then by Deduster 12 is removed.
Step 2) in after deduster 12 flue-gas temperature be 120 DEG C, connect the deduster 12 of the shell-side outlet pipeline of heater 22 Rear pass branch is located at the 3m behind the rear pass branch of deduster 12 of the connection shell side inlet pipeline of heater 22.
Step 2) in the heat transfer type of flue gas in heater 22 and waste water be countercurrent heat-transfer;On waste water in condenser 26 The heat transfer type of clear liquid and steam is countercurrent heat-transfer, and the shell side of heater 22 smears teflon coating.
Step 2) described in evaporator 20 temperature control at 55 DEG C, vacuum pressure is controlled in 0.0158MPa.
Step 2) described in by crystal seed add evaporator 20 in, be easy in waste water form crystal block.
Step 2) described in evaporator 20 overall density of waste water maintain 50%.
Step 2) described in the upper sieve plate 43 of gas washer 24 plate hole be 3.5mm, gas washing water thickness be 55 DEG C at saturation it is clear Water and thickness are 2mm.
Step 2) described in the internal diameter 7mm of sieve plate pipeline 42 in gas washer 24, demisting plate 41 is at intervals of 8mm.
Embodiment 2:
Low-temp low-pressure desulfurization wastewater vaporising device used in the present embodiment and above-described embodiment 1 are essentially identical, and distinguish as follows:
Described low-temp low-pressure desulfurization wastewater evaporation technology, is comprised the following steps that:
1) dedusting of deduster 12 is entered after flue gas reclaims used heat through air preheater 11, the flue gas after dedusting enters desulfurizing tower Desulfurization 13, produces desulfurization wastewater;
2) the desulfurization wastewater stoste for producing desulfurizing tower 13 injects water storage apparatus 30, after settlement, takes water storage apparatus 30 Wastewater supernatant fluid injects the tube side of condenser 26 through feed pump 31, and low pressure evaporation is injected after steam preheating in the tube side of condenser 26 Device 20, and mixed with the desulfurization wastewater with certain temperature in evaporator 20;Waste water is extracted out through sludge pump 1 and turned into after mixing Highly pressurised liquid, enters back into the heating of the tube side of heater 22, and waste water heating institute calorific requirement is come from after deduster 12 more than flue gas wherein at this Heat, flue gas walks the shell side of heater 22 with the waste water in tube side through row heat exchange;Waste water after heating sprays through high pressure atomizing nozzle 23 Go out to be formed hot waste water droplet and be again introduced into low pressure evaporator 20 to be flashed, the drop of formation steam and non-evaporating completely; The drop of non-evaporating completely is then dropped back on evaporator liquid level, and steam is then through gas washer 24 from the bottom to top by the plate of sieve plate 43 layer by layer Hole, gas washing water and demisting plate 41 remove tiny salt particle and droplet, clean steam are formed, then through the steam (vapor) outlet of gas washer 24 Into the shell side of condenser 26, wherein gas washing water is from top to bottom flowed into evaporator 20 through sieve plate pipeline 42, wherein flushing line 45 Periodically turn on, supply line 44 is persistently opened;The condensed shell side of device 26 of clean steam, is handed over the tube side wastewater supernatant fluid of condenser 26 Heat exchange amount, condensation forms condensed water, then is discharged by draining pump 27 for power plant's reuse, and in condenser 26 incoagulable gas then by Vavuum pump 25, which is extracted out, drains to maintain the vacuum of whole evaporation and crystallization system;When sludge concentration reaches setting value in evaporator 20 When, stop being evaporated in vacuo, the base sludge of evaporator 20 is discharged by residue extraction mechanism 28, extracted out through sludge pump 2 29, by atomizer The 32 flues evaporations sprayed into behind air preheaters 11, form steam and salt particle, steam is discharged with flue gas, salt particle then by except Dirt device 12 is removed.
Step 2) in after deduster 12 flue-gas temperature be 130 DEG C, connect the deduster 12 of the shell-side outlet pipeline of heater 22 Rear pass branch is located at the 3.5m behind the rear pass branch of deduster 12 of the connection shell side inlet pipeline of heater 22.
Step 2) in the heat transfer type of flue gas in heater 22 and waste water be countercurrent heat-transfer;On waste water in condenser 26 The heat transfer type of clear liquid and steam is countercurrent heat-transfer, and the shell side of heater 22 smears teflon coating.
Step 2) described in temperature control in evaporator 20 at 50 DEG C, vacuum pressure is controlled in 0.0124MPa.
Step 2) in by the crystal seed add evaporator 20 in, be easy in waste water form crystal block.
Step 2) described in evaporator 20 overall density of waste water maintain 45%.
Step 2) described in the upper sieve plate 43 of gas washer 24 plate hole be 4mm, gas washing water be 50 DEG C at saturation clear water and thickness Spend for 4mm.
Step 2) described in the internal diameter 6mm of sieve plate pipeline 42 in gas washer 24, demisting plate 41 is at intervals of 6mm.
It should be understood that above-described embodiment is only to illustrate technical concepts and features of the present utility model, its object is to supply ability Field technique personnel understand content of the present utility model and implemented according to this, and the not exhaustion of embodiment can not be limited with this Make protection domain of the present utility model.It is all to be modified according to technical scheme of the present utility model or equivalent substitution, and The objective and scope of technical solutions of the utility model are not departed from, it all should cover works as in right of the present utility model In.

Claims (3)

1. a kind of low-temp low-pressure desulfurization wastewater evaporating, the device includes flue gas processing system (1) and evaporation knot Crystallographic system unites (2).
The flue gas processing system (1) includes air preheater (11), deduster (12) and desulfurizing tower (13);
The evaporation and crystallization system (2) includes evaporator (20), sludge pump one (21), heater (22), high pressure atomizing nozzle (23), gas washer (24), vavuum pump (25), condenser (26), draining pump (27), residue extraction mechanism (28), sludge pump two (29), storage Wetting system (30), feed pump (31) and atomizer (32), wherein gas washer (24) include demisting plate (41), sieve plate pipeline (42), sieve plate (43), supply line (44) and flushing line (45);
Water storage apparatus (30) supernatant outlet in the evaporation and crystallization system (2) connects feed pump (31) entrance by the road;Institute State feed pump (31) outlet and connect condenser (26) tube-side inlet by the road;Condenser (26) the tube side outlet is connected by the road Evaporator (20) tank body;Evaporator (20) tank body connects sludge pump one (21) entrance by the road;The sludge pump one (21) Outlet connects heater (22) tube-side inlet by the road;Heater (22) the tube side outlet connects high pressure atomizing nozzle by the road (23);Heater (22) shell side inlet connects deduster (12) rear pass branch by the road;Heater (22) shell side Outlet connects deduster (12) rear pass branch by the road;The high pressure atomizing nozzle (23) is placed in evaporator (20) tank body Portion;Gas washer (24) main body connects evaporator (20) tank body through flange;Gas washer (24) steam (vapor) outlet connects by the road Connect condenser (26) shell side inlet;Condenser (26) shell-side outlet connects draining pump (27) entrance by the road;The vacuum Pump (25) bleeding point connects condenser (26) incoagulable gas outlet by the road;Evaporator (20) the deslagging outlet is by the road Connect residue extraction mechanism (28) entrance;Residue extraction mechanism (28) outlet connects sludge pump two (29) entrance by the road;The sludge Pump two (29) outlet connects atomizer (32) by the road;The atomizer (32) is arranged in air preheater (11) rear pass It is internal.
2. low-temp low-pressure desulfurization wastewater evaporating according to claim 1, it is characterised in that the evaporative crystallization Four pieces of sieve plates (43) and one piece of demisting plate (41) are spaced apart successively from the bottom to top inside gas washer (24) in system (2);Its Middle sieve plate pipeline (42) is fixed on sieve plate (43).
3. low-temp low-pressure desulfurization wastewater evaporating according to claim 1, it is characterised in that the evaporative crystallization Water storage apparatus (30) in system (2) is water tank.
CN201621383340.8U 2016-12-16 2016-12-16 A kind of low-temp low-pressure desulfurization wastewater evaporating Active CN206384875U (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110240212A (en) * 2019-07-09 2019-09-17 青岛达能环保设备股份有限公司 A kind of waste water evaporation concentration system and technique based on low temperature spray desulfurization
CN110272081A (en) * 2019-07-24 2019-09-24 北京新世翼节能环保科技股份有限公司 Desulfurization wastewater zero-emission coupling flue gas takes off white integral system

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110240212A (en) * 2019-07-09 2019-09-17 青岛达能环保设备股份有限公司 A kind of waste water evaporation concentration system and technique based on low temperature spray desulfurization
CN110272081A (en) * 2019-07-24 2019-09-24 北京新世翼节能环保科技股份有限公司 Desulfurization wastewater zero-emission coupling flue gas takes off white integral system
CN110272081B (en) * 2019-07-24 2023-12-22 北京新世翼节能环保科技股份有限公司 Desulfurization wastewater zero release coupling flue gas whitening integrated system

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