CN105621514A - Salt-containing wastewater concentration treatment device with air as medium - Google Patents
Salt-containing wastewater concentration treatment device with air as medium Download PDFInfo
- Publication number
- CN105621514A CN105621514A CN201610158397.6A CN201610158397A CN105621514A CN 105621514 A CN105621514 A CN 105621514A CN 201610158397 A CN201610158397 A CN 201610158397A CN 105621514 A CN105621514 A CN 105621514A
- Authority
- CN
- China
- Prior art keywords
- air
- water
- tower
- containing wastewater
- salt
- 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.)
- Pending
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/04—Treatment of water, waste water, or sewage by heating by distillation or evaporation
- C02F1/14—Treatment of water, waste water, or sewage by heating by distillation or evaporation using solar energy
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/04—Treatment of water, waste water, or sewage by heating by distillation or evaporation
- C02F1/08—Thin film evaporation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/04—Treatment of water, waste water, or sewage by heating by distillation or evaporation
- C02F1/16—Treatment of water, waste water, or sewage by heating by distillation or evaporation using waste heat from other processes
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/20—Controlling water pollution; Waste water treatment
- Y02A20/208—Off-grid powered water treatment
- Y02A20/212—Solar-powered wastewater sewage treatment, e.g. spray evaporation
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Sustainable Development (AREA)
- Sustainable Energy (AREA)
- Heat Treatment Of Water, Waste Water Or Sewage (AREA)
- Vaporization, Distillation, Condensation, Sublimation, And Cold Traps (AREA)
Abstract
The invention discloses a novel salt-containing wastewater concentration treatment device with air as a medium. The novel salt-containing wastewater concentration treatment device consists of a packed tower (evaporator), a plate heat exchanger (condenser) and a heating module (low-grade heat energy and solar energy), wherein a humidification and dehumidification method is adopted; flowing air is taken as a vapor carrier to treat salt-containing wastewater in an evaporation concentration manner; air is humidified by the heated salt-containing wastewater in the packed tower, is fed into the plate heat exchanger according to different temperature gradients in the packed tower after a certain amount of vapor is carried, and is condensed and dehumidified, so that fresh water can be produced; condensation latent heat can be recycled to preheat the salt-containing wastewater. (See the structure chart in the drawings of the description) By adopting the novel salt-containing wastewater concentration treatment device disclosed by the invention, the defects that a conventional treatment method is high in energy consumption, up-front cost and later maintenance cost, production scale requirement, and requirement on foundation facilities in a production area can be avoided.
Description
Technical field:
The present invention relates to and carry out concentrating to high-salt wastewater (total containing salt massfraction be 1%��3.5%) and obtain equipment and the technique thereof of fresh water, belong to the technical field of wastewater treatment, it is possible to be attributed to energy-saving and emission-reduction field.
Background technology
Fresh water belongs to basic natural resources and strategic economic resources, is the control selector of ecotope and the organic component of country's overall national strength. On the earth, only the water source of 3% can be drunk. The whole world about has the population of 25% to can not get enough fresh water, and the country more than 80% faces serious water resources shortage problem. Along with the expansion of world's arid and desertification, exacerbate the seriousness of water resources problems.
In order to tackle fresh water crisis, it is a kind of effective method that brine waste carries out concentration. Brine waste refers to always containing the inorganic salt waste water that salt massfraction is 1%��3.5%, and main source is the high-salt wastewater of seawater, underground shallow layer salt water, Industrial processes generation. Now main concentration method has multistage flash evaporation method, multiple-effect distillation, vapour compression method etc. Above-mentioned several method shortcoming mainly contain following some: 1, being consumed a large amount of electric power and fuel, on the one hand economy is poor, is unfavorable for economizing on resources on the other hand; 2, it is only suitable for scale operation, higher for cost for wastewater treatment on a small scale; 3, production unit drops into relatively big, and safeguards that these equipment needs bigger input; 4, most treatment process all needs just can carry out in area preferably in Infrastructure, is difficult in the area of poor infrastructure carry out. For the shortcoming of above several method, the wet waste water treatment process that dries that increases utilizing air to be medium in recent years obtains certain attention, this kind of method makes both waste water and carrier gas (being generally air) contact with each other, temperature and the humidity of carrier gas is improved with this, its condensation is obtained fresh water thereupon, raw material is concentrated, and condensation latent heat carries out the treatment process of effective recycling, increases the wet wastewater treatment equipment that dries and is generally made up of evaporator room, condensing chamber and heating module.
Packing tower is built with the gas-liquid mass transfer (contact) equipment of a large amount of fillers as alternate contact component taking tower. Waste water adds from tower top, pours on filler through shower nozzle spray, and flows down along filling surface. Gas is sent into from the bottom of tower, is the space that adverse current continues through filler with waste water. Surperficial gas-liquid two-phase at filler closely contacts and carries out mass transfer. Packing tower has that throughput is big, feature little, that liquid holdup is little, turndown ratio is big falls in separation efficiency height, pressure.
Plate-type heat exchanger is a kind of new type high efficient heat exchanger filled by a series of metal film stack with certain bellows-shaped. Form thin rectangular shape passage between various plate, carry out thermal exchange by plate. Plate-type heat exchanger is the ideal equipment that liquid-liquid, liquid-vapour carry out heat exchange. It has heat exchange efficiency height, thermosteresis is little, advantages of compact and light structure, floor space are little, install easy to clean, be widely used, the feature such as long service life. In uniform pressure loss situation, doubly, floor space is 1/3rd of tubular heat exchanger to its ratio of heat transfer coefficient tubular heat exchanger height 3-5, and heat recovery rate can up to more than 90%.
The present invention, using packing tower, plate-type heat exchanger as evaporator room, condensing chamber, selects suitable low grade residual heat, sun power to form sewage treatment equipment as heating module, and selects suitable working parameter according to different operating mode.
Summary of the invention
The present invention is directed to conventional concentration method consumed energy height, production cost input cost big, be unfavorable for small-scale production, need in the Infrastructure problem such as area preferably, utilize the principle increasing wet dehumidification, devise a kind of new concentration instrument and supplies.
The present invention is made up of packing tower (evaporator room), plate-type heat exchanger (condensing chamber), heating module. The technical scheme adopted is the carrier introducing flowing air as water vapour, and is separated with condensing chamber by evaporator room, and their temperature can independently be controlled; Air is increased wet in evaporator room by brine waste, enters in condensing chamber, obtain fresh water through dehumidification by condensation after carrying a certain amount of water vapour, and condensation latent heat is reclaimed by preheating brine waste. Heating module can utilize low grade residual heat and sun power to carry out energy supply. In order to obtain bigger treatment capacity, then several equipment can be carried out series connection combination producing.
The present invention is different from traditional salt-containing waste water treatment method, production cost and the treatment scale of the main flow treatment processs such as conventional treatment process such as multistage flash evaporation method, multiple-effect distillation, vapour compression method are closely related, relatively be applicable to large-scale treating processes, but these technology and be not suitable for process engineering on a small scale. And the input of purchase of equipment is relatively big in advance, and later maintenance cost is also higher. For the enterprise that some industrial scales are less, utilizing electric energy to carry out processing cost higher, particularly those have the enterprise enriching low grade residual heat, the treatment unit that urgent needs are compact simplified. Increasing the wet desalination techniques that dries and overcome an above difficult problem ingeniously, apparatus structure is simple, and does not consume fossil energy, is easy to operation and maintenance, although output is not as good as traditional method, but can carry out series connection production and supply.
Accompanying drawing explanation
Fig. 1 is the structural representation of the brine waste concentration device of the present invention.
Number in the figure illustrates: 1-fresh water pond for recovering, 2,3,4-plate-type heat exchanger, 5-heating module, 6-packing tower, 7-shower nozzle, 8-gas blower, 9-concentrated solution outlet, 10-feed reservoir, 11-pump, 12,13-water vapour pipeline, 14,15-fluid pipeline.
Embodiment
During the device start of the present invention, water pump 11, by brine waste suction system from feed reservoir 10, leads to heating module 5 via plate-type heat exchanger 2,3,4. Raw material flows to packing tower 6 after being heated to 70��90 DEG C by heating module 5, evenly is spilt by shower nozzle 7 and forms water smoke to inner-tower filling material; Now have in tower by tower pucking blower fan 8 blow into normal temperature air. High temperature feedstock water smoke fully contacts generation mass-and heat-transfer with air on filler, and absorption of air moisture is saturated gradually by unsaturated state, and the temperature of air is in constantly uphill process simultaneously, and wettability power is also in continuous enhancing. Raw material moisture constantly evaporates and scatters and disappears and concentration rising, reaches concentrated object, is finally discharged outside tower. The air of moist high temperature enters plate-type heat exchanger 2,3,4 by the different gradient segmentations of temperature, and carries out pre-warmed raw material and carries out heat exchange, becomes liquid water, heated by the raw material waste water of normal temperature simultaneously after steam coagulation. The wet air that in tower, temperature is higher temperature after higher level's interchanger is consistent with subordinate interchanger inlet temperature and mixes, with ingress of subordinate water vapour, the heat transfer process participating in next interchanger through pipeline 13, utilizes the condensation latent heat of water vapour to greatest extent. Flow process like this, until final product obtains concentrated solution and fresh water. Water vapour produces certain negative pressure in liquefaction process simultaneously, accelerates raw materials evaporate in packing tower 6.
Claims (3)
1. air is the wet dehumidification brine waste concentration device of increasing of medium, appliance arrangement comprises: 1-fresh water pond for recovering, 2,3,4-plate-type heat exchanger, 5-heating module, 6-packing tower, 7-shower nozzle, 8-gas blower, 9-concentrated solution outlet, 10-feed reservoir, 11-pump, 12,13-water vapour pipeline, 14,15-fluid pipeline. Water pump 11, by brine waste suction system from feed reservoir 10, leads to heating module 5 via plate-type heat exchanger 2,3,4. Raw material flows to packing tower 6 after being heated to 70��90 DEG C by heating module 5, evenly is spilt by shower nozzle 7 and forms water smoke to inner-tower filling material; Now have in tower by tower pucking blower fan 8 blow into normal temperature air. High temperature feedstock water smoke fully contacts generation mass-and heat-transfer with air on filler, and absorption of air moisture is saturated gradually by unsaturated state, and the temperature of air is in constantly uphill process simultaneously, and water-retaining capacity is also in continuous enhancing. Raw material moisture constantly evaporates and scatters and disappears and concentration rising, reaches concentrated object, is finally discharged outside tower. The air of moist high temperature enters plate-type heat exchanger 2,3,4 by the different gradient segmentations of temperature, and carries out pre-warmed raw material and carries out heat exchange, becomes liquid water, heated by the raw material waste water of normal temperature simultaneously after steam coagulation. The wet air that in tower, temperature is higher temperature after higher level's interchanger is consistent with subordinate interchanger inlet temperature and mixes, with ingress of subordinate water vapour, the heat transfer process participating in next interchanger through pipeline 13, utilizes the condensation latent heat of water vapour to greatest extent. Flow process like this, until final product obtains concentrated solution and fresh water. Water vapour produces certain negative pressure in liquefaction process simultaneously, accelerates raw materials evaporate in packing tower 6.
2. require according to right 1 that increasing wet dehumidification brine waste concentration device is characterized in that: it is multistage derivation structure (being generally three grades) that the water vapour on packing tower 6 derives structure, utilize this kind of structure can greatly utilize the heat in tower, and then improve the utilization of water vapor condensation latent heat.
3. require according to right 1 that increasing wet dehumidification brine waste concentration device is characterized in that: the carrier gas medium using the air of normal temperature and pressure as water vapour, these medium wide material sources, during plant running, physicochemical property are reliable and stable.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201610158397.6A CN105621514A (en) | 2016-03-18 | 2016-03-18 | Salt-containing wastewater concentration treatment device with air as medium |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201610158397.6A CN105621514A (en) | 2016-03-18 | 2016-03-18 | Salt-containing wastewater concentration treatment device with air as medium |
Publications (1)
Publication Number | Publication Date |
---|---|
CN105621514A true CN105621514A (en) | 2016-06-01 |
Family
ID=56036922
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201610158397.6A Pending CN105621514A (en) | 2016-03-18 | 2016-03-18 | Salt-containing wastewater concentration treatment device with air as medium |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN105621514A (en) |
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106451725A (en) * | 2016-09-26 | 2017-02-22 | 常州大学 | Solar energy and power-combined inorganic salt solution concentration system |
CN108178218A (en) * | 2018-03-21 | 2018-06-19 | 张建东 | A kind of Waste water concentrating liquid stream crystallizing and drying system and method for air direct emission |
CN108249497A (en) * | 2018-03-21 | 2018-07-06 | 张建东 | A kind of waste water airdistillation thickening-purification technology System and method for |
CN109052526A (en) * | 2018-08-28 | 2018-12-21 | 盛发环保科技(厦门)有限公司 | Flue gas disappears white coupling high temperature bypass flue evaporation high slat-containing wastewater Zero discharging system |
CN110117033A (en) * | 2019-05-16 | 2019-08-13 | 河北工业大学 | A kind of method and device of capillary low-temperature evaporation high slat-containing wastewater |
CN110451711A (en) * | 2019-08-13 | 2019-11-15 | 武汉宏澳绿色能源工程有限责任公司 | A kind of system and method for realizing high-salt wastewater condensing crystallizing using air air lift |
CN110540257A (en) * | 2018-05-29 | 2019-12-06 | 中国科学院广州能源研究所 | Coal fired power plant desulfurization waste water evaporative concentration and fresh water recovery device |
CN113426257A (en) * | 2021-06-08 | 2021-09-24 | 威海金宏科技有限公司 | Wastewater recovery process and system based on low-grade heat source |
CN113526594A (en) * | 2021-07-31 | 2021-10-22 | 董春 | Industrial wastewater desalting and desalting evaporator and desalting method |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2009072734A (en) * | 2007-09-23 | 2009-04-09 | Motohide Takezaki | Seawater desalting apparatus using air stream circulation |
WO2010063341A1 (en) * | 2008-12-02 | 2010-06-10 | Rolls-Royce Plc | Desalination method |
CN102205993A (en) * | 2011-03-18 | 2011-10-05 | 清华大学 | Adverse current closed type multistage seawater desalination system and method |
CN105174332A (en) * | 2015-07-16 | 2015-12-23 | 浙江大学 | Method for processing garbage leachate and device thereof |
-
2016
- 2016-03-18 CN CN201610158397.6A patent/CN105621514A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2009072734A (en) * | 2007-09-23 | 2009-04-09 | Motohide Takezaki | Seawater desalting apparatus using air stream circulation |
WO2010063341A1 (en) * | 2008-12-02 | 2010-06-10 | Rolls-Royce Plc | Desalination method |
CN102205993A (en) * | 2011-03-18 | 2011-10-05 | 清华大学 | Adverse current closed type multistage seawater desalination system and method |
CN105174332A (en) * | 2015-07-16 | 2015-12-23 | 浙江大学 | Method for processing garbage leachate and device thereof |
Cited By (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106451725A (en) * | 2016-09-26 | 2017-02-22 | 常州大学 | Solar energy and power-combined inorganic salt solution concentration system |
CN108178218A (en) * | 2018-03-21 | 2018-06-19 | 张建东 | A kind of Waste water concentrating liquid stream crystallizing and drying system and method for air direct emission |
CN108249497A (en) * | 2018-03-21 | 2018-07-06 | 张建东 | A kind of waste water airdistillation thickening-purification technology System and method for |
CN108178218B (en) * | 2018-03-21 | 2023-06-30 | 张建东 | System and method for crystallizing and drying wastewater concentrate by directly discharging air |
CN110540257A (en) * | 2018-05-29 | 2019-12-06 | 中国科学院广州能源研究所 | Coal fired power plant desulfurization waste water evaporative concentration and fresh water recovery device |
CN109052526A (en) * | 2018-08-28 | 2018-12-21 | 盛发环保科技(厦门)有限公司 | Flue gas disappears white coupling high temperature bypass flue evaporation high slat-containing wastewater Zero discharging system |
CN110117033A (en) * | 2019-05-16 | 2019-08-13 | 河北工业大学 | A kind of method and device of capillary low-temperature evaporation high slat-containing wastewater |
CN110117033B (en) * | 2019-05-16 | 2021-09-28 | 河北工业大学 | Method and device for evaporating high-salt-content wastewater at low temperature through capillary |
CN110451711A (en) * | 2019-08-13 | 2019-11-15 | 武汉宏澳绿色能源工程有限责任公司 | A kind of system and method for realizing high-salt wastewater condensing crystallizing using air air lift |
CN113426257A (en) * | 2021-06-08 | 2021-09-24 | 威海金宏科技有限公司 | Wastewater recovery process and system based on low-grade heat source |
CN113526594A (en) * | 2021-07-31 | 2021-10-22 | 董春 | Industrial wastewater desalting and desalting evaporator and desalting method |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN105621514A (en) | Salt-containing wastewater concentration treatment device with air as medium | |
Srithar et al. | Recent fresh water augmentation techniques in solar still and HDH desalination–A review | |
US8252092B2 (en) | Water separation under varied pressure | |
CN102010020B (en) | Solar energy sea water desalinization heat collecting system | |
US8465006B2 (en) | Separation of a vaporizable component under reduced pressure | |
CN1323032C (en) | Apparatus of combined solar energy heat pump for desaltination of sea water | |
CN101955238A (en) | Seawater desalting method and device | |
CN201634462U (en) | Seawater desalting device | |
CN103496750B (en) | System for concentrating salt-containing wastewater and recycling fresh water by comprehensive utilization of heat pump system | |
CN113023984A (en) | Desulfurization wastewater low-temperature concentration system and method | |
CN201587871U (en) | Multi-stage vacuum distillation sea water desalinating device | |
CN109020031B (en) | Evaporation concentration system based on thermal compression | |
CN203095658U (en) | Air humidifying and solution moisture absorbing solar freshwater preparation device | |
CN102329035A (en) | Fresh water collecting and supplying system | |
CN202116341U (en) | Small-sized solar seawater desalinization device | |
CN101125673A (en) | Method for directly producing calcium chloride from ammonia-soda process waste liquid | |
CN104528850A (en) | Trigeneration system of fresh water, sea salt and heat energy based on deep concentration of sea water desalination strong brine | |
CN108328684B (en) | Multistage seawater desalination system based on carrier gas humidity change | |
CN104649493A (en) | Method and system for treating high-concentration wastewater by virtue of low-temperature evaporative crystallization | |
CN106915792A (en) | Wind-solar complementary seawater desalination device | |
CN201660457U (en) | Novel multiple-effect distilled sea water desalination device | |
CN201373694Y (en) | Combined secondary steam heat energy recovery device for heat pipe phase change heat exchanger of steam jet heat pump | |
CN108128831A (en) | Solar heat pump desalination plant | |
CN201882942U (en) | Power-generation turboset condenser type sea water desalinating unit | |
CN203568872U (en) | Aqueous solution phase change separation 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 | ||
WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20160601 |
|
WD01 | Invention patent application deemed withdrawn after publication |