CN105439221B - The condensing crystallizing processing system and method for a kind of boiler drum sewerage - Google Patents

The condensing crystallizing processing system and method for a kind of boiler drum sewerage Download PDF

Info

Publication number
CN105439221B
CN105439221B CN201510994516.7A CN201510994516A CN105439221B CN 105439221 B CN105439221 B CN 105439221B CN 201510994516 A CN201510994516 A CN 201510994516A CN 105439221 B CN105439221 B CN 105439221B
Authority
CN
China
Prior art keywords
control valve
salt
drum
reactor
pressure reducing
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CN201510994516.7A
Other languages
Chinese (zh)
Other versions
CN105439221A (en
Inventor
张乃强
岳国强
许尧
曹琦
蒋东方
朱忠亮
吕法彬
徐鸿
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
North China Electric Power University
Original Assignee
North China Electric Power University
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 North China Electric Power University filed Critical North China Electric Power University
Priority to CN201510994516.7A priority Critical patent/CN105439221B/en
Publication of CN105439221A publication Critical patent/CN105439221A/en
Application granted granted Critical
Publication of CN105439221B publication Critical patent/CN105439221B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F2001/5218Crystallization

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)

Abstract

The invention belongs to power station water process and energy resource recycling technical field, the condensing crystallizing processing system and method for more particularly to a kind of boiler drum sewerage.The system is made of drum, blowdown control valve, booster pump, reactor water inlet control valve, supercritical water separate reactor, heater, pressure reducing valve I, salt discharge control valve, pressure reducing valve II and salt collection device.The present invention realizes the separation of salt, water, while realize the recycling recycled with energy of sewerage, a kind of green, pollution-free, efficient new method is provided for steam boiler continuous blowdown water process without outside plus under conditions of any catalyst.

Description

The condensing crystallizing processing system and method for a kind of boiler drum sewerage
Technical field
The invention belongs to power station water process and energy resource recycling technical field, more particularly to a kind of boiler vapour The condensing crystallizing processing system and method for packet sewerage.
Background technology
Currently, with the growth of China human mortality and the quickening of urbanization, the utilization of water resource approaches it substantially Supply amount, water crisis phenomenon increasingly show.In addition people's life and industrial water are continuously increased, and water resource supply is difficult for After, and water environment pollution more deteriorates.Only develop water resource recycle economy, realize cycling utilization of wastewater, could really protect It protects water environment, cut down water pollution.
Not only quantity is big for continuous blowdown system of boiler, but also temperature, pressure are higher, and the economic value of recycling is larger.Continuously Blowdown is also known as surface blow-off, it is desirable that the larger stove water of salt concentration is continuously excluded from drum, including iron ion, copper from Son, potassium ion, sodium ion, carbanion and chlorion etc., to reduce the corrosion to heat power equipment.It is continuous for dum boiler Blowdown, traditional way are to install a continuous blowdown expander additional, and sewerage carries out volume-expanding pressure-reducing, rapid shape after entering expander Water is heated into indirect steam and being introduced into thermal deaerator or feed-tank.Remaining saturated water drains into blowdown expander Blowdown cooling tank enters municipal drainage network with tap water hybrid cooling heel row.
The shortcomings that this method is:(a) still carry very big energy by the sewerage of blowdown expander cannot utilize, (b) a large amount of tap water is wasted to cool down sewerage.Many power plant dum boiler does not have blowdown dilatancy in actual motion Device or flash vessel do not come into operation, and sewerage is exhausted directly to after the cooling of blowdown cooling tank outside factory.According to《If rule》Regulation, The normal blowdown rate of condensing power plant's boiler is no more than 1%, and the normal blowdown rate of heat-supply type thermal power plant boiler is no more than 2%.With For 300MW condensing-type generating sets, boiler capacity 1000t/h, if blowdown rate is 1%, the water amount of blowdown of 1 year is 8.76×104T, these high temperature and pressure drum sewerage direct emissions not only cause the waste at water source, but also a large amount of Gao Pin Potential energy is lost.
Supercritical water (Supercritical Water, abbreviation SCW) refers to temperature more than 374.15 DEG C, and pressure is more than The water of the special state of 22.12MPa, at this time the density value of water, dielectric constant, ionic product decline, hydrogen bond reduce so that water into For a kind of apolar medium or even the gentle physical efficiency of nonpolar organic matter with high diffusibility and excellent transmission characteristic and water with Arbitrary proportion dissolves each other, and forms single homogeneous system, this causes solubility of the salt in supercritical water to be remarkably decreased.
Sewerage increasing temperature and pressure is above-critical state using this characteristic by the present invention, is utilized in overcritical separate reactor Salt condensing crystallizing is precipitated in the property of supercritical water, and sewerage can be effectively treated in the present invention, to reach high-efficiency environment friendly, resource The energy conservation and environmental protection theory of heat recovery.
Invention content
The present invention provides the condensing crystallizing processing systems and method of a kind of boiler drum sewerage, and specific technical solution is such as Under:
A kind of condensing crystallizing processing system of boiler drum sewerage, by drum 1, blowdown control valve 2, booster pump 3, reaction Device water inlet control valve 4, supercritical water separate reactor 5, heater 6, pressure reducing valve I 7, salt discharge control valve 8,9 and of pressure reducing valve II Salt collection device 10 forms;The drum 1, blowdown control valve 2, booster pump 3, reactor water inlet control valve 4 and supercritical water Separate reactor 5 is sequentially connected with, and supercritical water separate reactor 5 is coated with heater 6;Supercritical water separate reactor 5 Upper outlet is divided into two-way, and a-road-through crosses pressure reducing valve I 7 and is connected with drum 1, and a-road-through crosses pressure reducing valve II 9 and collects dress with salt 10 are put to be connected;The lower part outlet of supercritical water separate reactor 5 is connected by salt discharge control valve 8 with salt collection device 10.
The method that the condensing crystallizing processing of boiler drum sewerage is carried out using system as described above, specific steps are such as Under:
Blowdown control valve 2, reactor water inlet control valve 4 and pressure reducing valve I 7 are opened, simultaneously close off salt discharge control valve 8 and is subtracted Pressure valve II9;The sewerage of drum 1 is pressurizeed, pressure is increased to critical pressure 22.1MPa by blowdown control valve 2 through booster pump 3 More than, excess of imports critical separate reactor 5 of going forward side by side, heater 6 by the temperature of saliferous subcritical water be increased to 374 DEG C of critical point with On, at this point, drum sewerage becomes above-critical state from subcritical state;
Since solubility of the salt in supercritical water drastically reduces, the salt condensing crystallizing in saliferous stove water is precipitated, and sinks It forms sediment in 5 bottom of supercritical water separate reactor, isolated above-critical state steam is depressured through pressure reducing valve Ι 7 from saliferous stove water Drum 1 is returned afterwards;
The salt for being deposited in 5 bottom of supercritical water separate reactor accumulates to supercritical water separate reactor (5) total volume 1/4 when, close blowdown control valve 2, booster pump 3, reactor water inlet control valve 4 and pressure reducing valve Ι 7, open pressure reducing valve II 9, adjust Section outlet pressure is 0.1MPa, and it is 0.2MPa to adjust pressure in supercritical water separate reactor 5, closes pressure reducing valve II 9 at this time, Salt discharge control valve 8 is opened simultaneously, the salt for being deposited in supercritical water separate reactor 5 is discharged into salt under differential pressure action receives In acquisition means 10;
After discharge, salt discharge control valve 8 is closed, opens reactor water inlet control valve 4, blowdown control valve 2 successively, simultaneously Start booster pump 3, open reactor steam discharge control valve 7, carry out second and recycle.
So cycle, the sewerage that this system detaches drum by discontinuity achieve the purpose that salt, water detach.
Further, for the drum sewerage after the pressurization of booster pump 3, pressure is increased to 23-24MPa.
Further, the temperature of saliferous subcritical water is increased to 380-400 DEG C by heater 6.
Beneficial effects of the present invention are:The present invention provides a kind for the treatment of effeciency is high, no pollution discharge, it is easy to operate, into This is low, and the condensing crystallizing processing system of the supercritical water separation boiler drum sewerage of resource and energy recovery can be achieved at the same time And method.Compared with conventional method, in present system, seldom a part of pressure energy is only lost when by pressure reducing valve, is avoided The waste of energy, greatly improves economy.
The present invention realizes the separation of salt, water, while realize sewerage without outside plus under conditions of any catalyst The recycling with energy is recycled, a kind of green, pollution-free, efficient new side is provided for dum boiler continuous blowdown water process Method.
Description of the drawings
Fig. 1 is the condensing crystallizing processing system structure diagram of the boiler drum sewerage of the present invention;
The meaning of each label is in figure:1- drums, 2- blowdown control valves, 3- booster pumps, 4- reactor water inlet control valves, 5- Supercritical water separate reactor, 6- heaters, 7- pressure reducing valves Ι, 8- salt discharge control valve, 9- pressure reducing valves II, 10- salt collect dress It puts.
Specific embodiment
The present invention is described further below in conjunction with the accompanying drawings.
A kind of condensing crystallizing processing system of boiler drum sewerage, by drum 1, blowdown control valve 2, booster pump 3, reaction Device water inlet control valve 4, supercritical water separate reactor 5, heater 6, pressure reducing valve I 7, salt discharge control valve 8,9 and of pressure reducing valve II Salt collection device 10 forms;The drum 1, blowdown control valve 2, booster pump 3, reactor water inlet control valve 4 and supercritical water Separate reactor 5 is sequentially connected with, and supercritical water separate reactor 5 is coated with heater 6;Supercritical water separate reactor 5 Upper outlet is divided into two-way, and a-road-through crosses pressure reducing valve I 7 and is connected with drum 1, and a-road-through crosses pressure reducing valve II 9 and collects dress with salt 10 are put to be connected;The lower part outlet of supercritical water separate reactor 5 is connected by salt discharge control valve 8 with salt collection device 10.
The method that the condensing crystallizing processing of boiler drum sewerage is carried out using system as described above, specific steps are such as Under:
Blowdown control valve 2, reactor water inlet control valve 4 and pressure reducing valve I 7 are opened, simultaneously close off salt discharge control valve 8 and is subtracted Pressure valve II 9;The continuous blowdown water of drum 1 is pressurizeed through booster pump 3 by blowdown control valve 2, and pressure is increased to 23-24MPa, and Into supercritical water separate reactor 5, the temperature of saliferous subcritical water is increased to 380-400 DEG C by heater 6, at this point, drum Sewerage becomes above-critical state from subcritical state;
Since solubility of the salt in supercritical water drastically reduces, the salt condensing crystallizing in saliferous stove water is precipitated, and sinks It forms sediment in 5 bottom of supercritical water separate reactor, isolated above-critical state steam is depressured through pressure reducing valve Ι 7 from saliferous stove water Drum 1 is returned afterwards;
The salt for being deposited in 5 bottom of supercritical water separate reactor accumulates to supercritical water separate reactor (5) total volume 1/4 when, close blowdown control valve 2, booster pump 3, reactor water inlet control valve 4 and pressure reducing valve Ι 7, open pressure reducing valve II 9, adjust Section outlet pressure is 0.1MPa, and it is 0.2MPa to adjust pressure in supercritical water separate reactor 5, closes pressure reducing valve II 9 at this time, Salt discharge control valve 8 is opened simultaneously, the salt for being deposited in supercritical water separate reactor 5 is discharged into salt under differential pressure action receives In acquisition means 10;
After discharge, salt discharge control valve 8 is closed, opens reactor water inlet control valve 4, blowdown control valve 2 successively, simultaneously Start booster pump 3, open reactor steam discharge control valve 7, carry out second and recycle.
So cycle, the sewerage that this system detaches drum by discontinuity achieve the purpose that salt, water detach.

Claims (3)

  1. A kind of 1. method of the condensing crystallizing processing of a kind of boiler drum sewerage, which is characterized in that the method is based on pot What the condensing crystallizing processing system of stove drum sewerage carried out, the system is by drum (1), blowdown control valve (2), booster pump (3), reactor water inlet control valve (4), supercritical water separate reactor (5), heater (6), pressure reducing valve I (7), salt discharge control valve (8), pressure reducing valve II (9) and salt collection device (10) composition;It is the drum (1), blowdown control valve (2), booster pump (3), anti- Device water inlet control valve (4) and supercritical water separate reactor (5) is answered to be sequentially connected with, supercritical water separate reactor (5) outer cladding Having heaters (6);The upper outlet of supercritical water separate reactor (5) is divided into two-way, and a-road-through crosses pressure reducing valve I (7) and drum (1) it is connected, a-road-through crosses pressure reducing valve II (9) and is connected with salt collection device (10);The lower part of supercritical water separate reactor (5) Outlet is connected by salt discharge control valve (8) with salt collection device (10);
    The method is as follows:
    Open blowdown control valve (2), reactor water inlet control valve (4) and pressure reducing valve I (7), simultaneously close off salt discharge control valve (8) and Pressure reducing valve II (9);The sewerage of drum (1) is pressurizeed, pressure is increased to critical pressure by blowdown control valve (2) through booster pump (3) The temperature of saliferous subcritical water is increased to by more than power 22.1MPa, excess of imports critical separate reactor (5) of going forward side by side, heater (6) 374 DEG C of critical point or more, at this point, drum sewerage becomes above-critical state from subcritical state;
    Since solubility of the salt in supercritical water drastically reduces, the salt condensing crystallizing in saliferous stove water is precipitated, and is deposited in Supercritical water separate reactor (5) bottom, isolated above-critical state steam is depressured through pressure reducing valve Ι (7) from saliferous stove water Drum (1) is returned afterwards;
    The salt for being deposited in supercritical water separate reactor (5) bottom accumulates to supercritical water separate reactor (5) total volume When 1/4, blowdown control valve (2), booster pump (3), reactor water inlet control valve (4) and pressure reducing valve Ι (7) are closed, opens pressure reducing valve II (9), adjusting outlet pressure are 0.1MPa, and it is 0.2MPa to adjust pressure in supercritical water separate reactor (5), close subtract at this time Pressure valve II (9), while salt discharge control valve (8) is opened, the salt of supercritical water separate reactor (5) will be deposited under differential pressure action Class is discharged into salt collection device (10);
    After discharge, salt discharge control valve (8) is closed, opens reactor water inlet control valve (4), blowdown control valve (2) successively, together Shi Qidong booster pumps (3) open reactor steam discharge control valve (7), carry out second and recycle.
  2. 2. according to the method described in claim 1, it is characterized in that, the drum sewerage through booster pump (3) pressurization after, pressure It is increased to 23-24MPa.
  3. 3. according to the method described in claim 1, it is characterized in that, the temperature of saliferous subcritical water is increased to by heater (6) 380-400℃。
CN201510994516.7A 2015-12-25 2015-12-25 The condensing crystallizing processing system and method for a kind of boiler drum sewerage Expired - Fee Related CN105439221B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510994516.7A CN105439221B (en) 2015-12-25 2015-12-25 The condensing crystallizing processing system and method for a kind of boiler drum sewerage

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510994516.7A CN105439221B (en) 2015-12-25 2015-12-25 The condensing crystallizing processing system and method for a kind of boiler drum sewerage

Publications (2)

Publication Number Publication Date
CN105439221A CN105439221A (en) 2016-03-30
CN105439221B true CN105439221B (en) 2018-06-22

Family

ID=55549941

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510994516.7A Expired - Fee Related CN105439221B (en) 2015-12-25 2015-12-25 The condensing crystallizing processing system and method for a kind of boiler drum sewerage

Country Status (1)

Country Link
CN (1) CN105439221B (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105864743A (en) * 2016-05-26 2016-08-17 清华大学 Pollution discharge, water and energy saving, recovery and separation device and method of steam injection boiler
CN113264562B (en) * 2021-04-27 2022-08-09 西安交通大学 Salt removing device and method for supercritical reaction of high-salinity water

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1363522A (en) * 2001-01-08 2002-08-14 深圳市宝利达实业有限公司 Process and equipment for supercritical desalination of sea water while providing energy
CN102190362A (en) * 2011-05-12 2011-09-21 西安交通大学 Supercritical water oxidation reaction system for obtaining heat supplemented by auxiliary fuel
CN202852790U (en) * 2013-01-11 2013-04-03 山东鲁花浓香花生油有限公司 Boiler blow-off residual heat utilization system
CN204550115U (en) * 2015-03-19 2015-08-12 济南长城炼油有限责任公司 A kind of steam drum sewage recycling device

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3502819B2 (en) * 2000-08-25 2004-03-02 石川県 Cosmetic containing extract extracted by making it supercritical fluid and method for producing the same

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1363522A (en) * 2001-01-08 2002-08-14 深圳市宝利达实业有限公司 Process and equipment for supercritical desalination of sea water while providing energy
CN102190362A (en) * 2011-05-12 2011-09-21 西安交通大学 Supercritical water oxidation reaction system for obtaining heat supplemented by auxiliary fuel
CN202852790U (en) * 2013-01-11 2013-04-03 山东鲁花浓香花生油有限公司 Boiler blow-off residual heat utilization system
CN204550115U (en) * 2015-03-19 2015-08-12 济南长城炼油有限责任公司 A kind of steam drum sewage recycling device

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
超(近)临界水中无机盐的脱除;单祥雷;《华南理工大学学报(自然科学版)》;20071031;第33卷(第5期);第606-609,638页 *

Also Published As

Publication number Publication date
CN105439221A (en) 2016-03-30

Similar Documents

Publication Publication Date Title
CN203128593U (en) Efficient blast furnace slag-washing water waste heat recycling system adopting INBA process
CN202023706U (en) Device for carrying out flash evaporation electricity generation and recovering distilled water by using terrestrial heat
CN201737726U (en) Solar seawater-desalinating device adopting passive flash evaporation technique
CN101303201A (en) Method of waste heat recovery utilization in cheese dyeing course
CN203731530U (en) Recycling system of boiler discharge water thermal energy and steam condensation water
CN105439221B (en) The condensing crystallizing processing system and method for a kind of boiler drum sewerage
CN103111082A (en) High-efficiency and energy-saving honey concentration technology and equipment and production system
CN204612228U (en) A kind of low temperature heat system
CN202132931U (en) System for recycling residual heat of discharged sewage of boiler
CN101792190B (en) Novel solar seawater desalination system
CN205031921U (en) Strip tower flash steam's heat energy and solvent recycling system
CN102583861B (en) Method for preheating inflow water of membrane method seawater softening device
CN204851350U (en) Utilize living water heating system of power plant's exhaust steam waste heat
CN104864597A (en) Three-phase heat exchanging self-insulation device
CN205014337U (en) A water supply equipment for improving waste heat power generation system heat exchange efficiency
CN212712829U (en) Solar photo-thermal seawater desalination integrated system
CN110422900B (en) Solar automatic sewage treatment system and working method thereof
CN203529968U (en) Solar wind-power combination seawater desalination device
CN112161407A (en) Heat exchange energy-saving system and method for regenerative system of solar thermal-coupled thermal power generating unit
CN202221246U (en) Slag heat recovery system
CN204174054U (en) Solar energy high temperature thermal hydrolysis associating flash-evaporation dehydration sludge treating system
CN205045838U (en) Distilled water device
CN204607766U (en) A kind of Waste water concentrating system
CN114810242B (en) Comprehensive utilization method and system for energy of back pressure turbine steam source
CN211084880U (en) Steam condensate water recycling system

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20180622

Termination date: 20181225