CN205838604U - A kind of thermal evaporation enrichment facility for processing membrance concentration liquid - Google Patents

A kind of thermal evaporation enrichment facility for processing membrance concentration liquid Download PDF

Info

Publication number
CN205838604U
CN205838604U CN201620744884.6U CN201620744884U CN205838604U CN 205838604 U CN205838604 U CN 205838604U CN 201620744884 U CN201620744884 U CN 201620744884U CN 205838604 U CN205838604 U CN 205838604U
Authority
CN
China
Prior art keywords
membrance concentration
concentration liquid
liquid
evaporation tank
sidewall
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
CN201620744884.6U
Other languages
Chinese (zh)
Inventor
宋薇
丁兆勇
刘晶昊
尹水娥
蒲志红
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.)
China Urban Construction Design and Research Institute Co Ltd
Original Assignee
China Urban Construction Design and Research Institute Co Ltd
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 China Urban Construction Design and Research Institute Co Ltd filed Critical China Urban Construction Design and Research Institute Co Ltd
Priority to CN201620744884.6U priority Critical patent/CN205838604U/en
Application granted granted Critical
Publication of CN205838604U publication Critical patent/CN205838604U/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)

Abstract

This utility model belongs to Pollutant Treatment technical field, provide a kind of thermal evaporation enrichment facility for processing membrance concentration liquid, including: evaporation tank, sidewall is provided with flue installing hole and liquid-inlet, top is provided with gas outlet, and sidewall bottom is provided with liquid outlet;Heat smoke admission line, enters evaporation tank through the flue installing hole on the sidewall of evaporation tank, and smoke inlet pipe road is positioned on the tube wall of evaporation tank and is provided with air-vent;Membrance concentration liquid enter pipeline, membrance concentration liquid enter pipeline through evaporation tank sidewall on liquid-inlet enter evaporation tank, membrance concentration liquid enter pipeline be positioned on the tube wall of evaporation tank arrange porose;The liquid outlet that the sidewall bottom of discharge line, discharge line and evaporation tank is arranged is connected.This utility model can make full use of discarded smoke discharging residual heat, had both decreased energy resource consumption, has reclaimed the water resource of preciousness, has made again membrance concentration liquid minimizing.

Description

A kind of thermal evaporation enrichment facility for processing membrance concentration liquid
Technical field
This utility model belongs to Pollutant Treatment technical field, particularly to a kind of thermal evaporation for processing membrance concentration liquid Enrichment facility.
Background technology
Percolate refers to that rubbish is being stacked and during landfill due to biochemical degradations such as compacting, fermentations, exists simultaneously The liquid of the organic or inorganic composition of a kind of high concentration produced under the seepage effect of precipitation and subsoil water, the most almost all of Percolate both is from refuse landfill and incineration plant.
Percolate, due to complicated component, containing multiple poisonous and hazardous inorganic matter and Organic substance, also contains in percolate There are non-chlorinated aromatic compound, chlorinated aromatic compounds of group such as being difficult to biodegradable naphthalene, phenanthrene, phosphoric acid vinegar, phenolic compound With amino benzenes compounds etc..In percolate, CODcr, BOD5 concentration peak is up to thousands of to several ten thousand, and municipal sewage phase Ratio, concentration is high, so percolate is to be directly discharged into municipal sewage treatment pipe without strict process, disposal Road.It is said that in general, CODcr, BOD5, BOD5/CODcr increase with " age " of landfill yard and reduce, level of alkalinity then raises. So percolate could be discharged after treatment.
The mode that landfill yard and incineration leachate use integrated treatment at present is the most, the most all uses early stage to locate in advance Aerobic Process for Treatment, ultrafiltration the most again, nanofiltration and reverse osmosis after first anaerobism after reason.Macromole and float can be leached, thoroughly by ultrafiltration That crosses ultrafilter membrane is mainly composed of humic acid and various little molecule and Ca2+、Mg2+、Na+、Cl-、CO2-、SO4 2-Plasma, needs Enter nanofiltration to process further;Almost all of humic acid and bivalence and above ion isolation are gone out by NF membrane, isolated dense Contracting liquid accounts for entering the 20% of nanofiltration.Nanofiltration concentrated solution is higher due to salinity and organic concentration, it is not easy to deposits or fills, Need to process further.Through the solution of NF membrane due to containing higher Na+、Cl-Deng monovalent ion, not up to discharge standard, Need nonetheless remain for processing further, therefore also need to reverse osmosis process.Clear liquid after reverse-osmosis treated is permissible after reaching discharge standard Discharging or for government utility pouring etc., reverse osmosis concentrated liquid accounts for entering about the 25% of the total amount of counter-infiltration system, main Wanting composition is Na+、Cl-Solution Deng monovalent ion.
For reverse osmosis concentrated liquid, owing to contaminative is relatively low, in the way of can filling again after taking natural air drying, but lean on Natural air drying is inefficient, floor space is bigger;Nacl can also be become by processes, but relatively costly;All right By the way of heat treatment concentrates, promote evaporation, but select the improper heat exchange contact surface that easily causes of Technology for Heating Processing to crystallize, lead Cause heating surface heat conduction inequality, heat transfer effect declines.
Process to nanofiltration concentrated solution, some technique is taked backflow to reenter percolation liquid treating system, is taked this kind of side Although formula can reduce the total amount of humic acid, but be as cycle-index and increase, Ca2+、Mg2+、CO2-、SO4 2-Plasma concentration liter Height, impacts the percolation liquid treating system before nanofiltration, so backflow can not finally solve nanofiltration concentrated solution;Spray into rubbish Burn burner hearth and heating surface can be caused corrosion and scale damage;Recharge landfill yard to be the most also intended to be again introduced into percolate.Cause These various processing methods researching and solving nanofiltration concentrated solution and technique are arisen at the historic moment.
Nanofiltration concentrated solution and reverse osmosis concentrated liquid are referred to as membrance concentration liquid.
The outer typical method disposing membrance concentration liquid of Present Domestic recharges, Membrane Materials, evaporation, advanced oxidation etc..But Actual motion application have also discovered some problems.
Recharge method.Recharge and can improve the response rate, increase membrane surface flushing flow velocity;But the fraud As time goes on, recharged End gradually displays, and domestic refuse landfill occurs in that the accumulation of pollutant the most in various degree, and percolate electrical conductivity raises, film Producing water ratio declines, and electrical conductivity even occur increases the problem causing membrane filtration to lose efficacy.
Membrane Materials method i.e. submerged combustion evaporation technology, is a kind of nothing evaporation mode of fixing heat-transfer area, by fuel and air Send into against liquid level or be immersed in the combustor under liquid level and burn completely, then high-temperature flue gas is injected directly into liquid it In to add hot liquid.High-temperature flue gas enters and rises with a large amount of minute bubbles forms after liquid, due to flue gas and liquid mixing with stir Dynamic very strong, thus significantly enhance diabatic process, tail gas is down to temperature much the same with liquid phase before discharge, heat transfer Efficiency may be up to more than 95%.
Evaporation is at certain temperature and pressure, and the most volatile Component seperation in mixed solution is gone out Method.Evaporation treatment process can be by the volume concentration of pending solution to the 2%~10% of not enough stock solution volume.
Advanced oxidation processes.For Mu Qian, the most several technology, high-level oxidation technology is to process percolate, film The reasonable selection of concentrated solution, has the most a little: 1. efficient, and the speed of high-level oxidation technology degradation of organic substances is very fast, and this is Other several technology cannot be compared.2. product harmless, the intermediate product in advanced oxidation processes oxidizing process all can continue same Hydroxyl radical reaction, until being finally oxidized to carbon dioxide and water completely, thus has reached the thorough mesh removing TOC, COD 's.3. it is a kind of physical and chemical process due to it, it is easy to be controlled by, with satisfied process needs.
Above-mentioned several method has employing in membrance concentration liquid processes, but all dense without reference to utilizing waste heat evaporation process film The device of contracting liquid, it is impossible to effectively utilize fume afterheat.
Utility model content
The purpose of this utility model is to provide a kind of thermal evaporation enrichment facility for processing membrance concentration liquid, at least to solve Prior art certainly exists the technical problem of the wasting of resources, can solve the problem that in prior art that there is membrance concentration liquid cannot reclaim simultaneously The technical problem utilized.
This utility model provides a kind of thermal evaporation enrichment facility for processing membrance concentration liquid, including:
Evaporation tank, the sidewall of described evaporation tank is provided with flue installing hole and liquid-inlet, and top is provided with out QI KOU, sidewall bottom is provided with liquid outlet;
Heat smoke admission line, described heat smoke admission line is installed through the flue on the sidewall of described evaporation tank Hole enters described evaporation tank, and described heat smoke admission line is positioned on the tube wall of described evaporation tank and is provided with air-vent, is used for Heat smoke is entered in described evaporation tank;
Membrance concentration liquid enters pipeline, and described membrance concentration liquid enters pipeline through the liquid-inlet on the sidewall of described evaporation tank Enter described evaporation tank, described membrance concentration liquid enter pipeline be positioned at arrange on the tube wall of described evaporation tank porose, for by film Concentrated solution enters in described evaporation tank;
The liquid outlet that the sidewall bottom of discharge line, described discharge line and described evaporation tank is arranged is connected, and is used for arranging Membrane concentrated solution dope.
Preferably, the flue installing hole that the sidewall of described evaporation tank is arranged is higher than liquid-inlet, so that institute The position stating heat smoke admission line enters pipeline higher than described membrance concentration liquid.
Preferably, described heat smoke admission line extends after the flue installing hole on the sidewall of described evaporation tank Offside sidewall to described evaporation tank.
Preferably, described heat smoke admission line gos deep into the bottom of described evaporation tank and/or downside has air-vent, makes Obtain heat smoke to spray from bottom and/or downside.
Preferably, described heat smoke admission line is one or more;It is one or many that described membrance concentration liquid enters pipeline Root;The liquid outlet that the sidewall bottom of described evaporation tank is arranged is multiple, and each described liquid outlet is all connected with a discharge pipe Road;It is further preferred that be additionally provided with pump on each described discharge line, in order to the membrance concentration liquid after concentrating is taken out Row.
Preferably, also including: anti-disturbance orifice plate, described anti-disturbance orifice plate is arranged on the flue of described evaporation tank and installs Bottom, hole, described anti-disturbance orifice plate is flat board, and flat board is provided with multiple hole.
Preferably, also including: anti-disturbance distribution grid, described anti-disturbance distribution grid is arranged on described membrance concentration liquid and enters pipeline The mouth of pipe below.
Preferably, described anti-disturbance distribution grid is flat board, and described anti-disturbance distribution grid enters pipe apart from described membrance concentration liquid The mouth of pipe 2mm in road.
Preferably, also including: condenser, described condenser is connected with described gas outlet, is used for receiving the evaporation of membrance concentration liquid The mixture of the cold flue gas that the steam formed and heat smoke are formed after heat exchange, and this mixture is cooled down so that it is In vaporous water condensation become aqueous water.
Preferably, described membrance concentration liquid includes nanofiltration concentrated solution and reverse osmosis concentrated liquid, when described membrance concentration liquid is nanofiltration During concentrated solution, described device also includes:
Pre-procesor, for carrying out preposition process to nanofiltration concentrated solution;Described pre-procesor includes:
Regulation container, is used for accommodating nanofiltration concentrated solution, adds NaOH in described regulation container, is used for reducing nanofiltration and concentrates Ca in liquid2+、Mg2+, nanofiltration concentrated solution is layered formation upper clear supernate layer in described regulation container and bottom concentrates liquid layer, institute State bottom and concentrate the liquid layer described heat exchanger of entrance;With
Humic sorrel extraction system, is used for absorbing described upper clear supernate layer.
The thermal evaporation enrichment facility being used for processing membrance concentration liquid of this utility model offer can make full use of discarded row Cigarette waste heat, had both decreased energy resource consumption, has reclaimed the water resource of preciousness, has made again membrance concentration liquid minimizing.
Other feature and advantage of the present utility model will describe in detail in following detailed description of the invention part.
Accompanying drawing explanation
Fig. 1 is the structural representation of the thermal evaporation enrichment facility for processing membrance concentration liquid of this utility model preferred embodiment Figure.
Wherein, the description of reference numerals in figure is as follows:
1-evaporation tank;11-gas outlet;2-heat smoke admission line;3-membrance concentration liquid enters pipeline;4-anti-disturbance orifice plate; 5-anti-disturbance distribution grid;6-discharge line.
Detailed description of the invention
For making the purpose of this utility model, technical scheme and advantage clearer, new to this practicality below in conjunction with accompanying drawing The embodiment of type is described in further detail.It should be appreciated that detailed description of the invention described herein is only used for Bright and explain this utility model, be not limited to this utility model.
In this utility model, membrance concentration liquid refers to nanofiltration concentrated solution and reverse osmosis concentrated liquid.
As it is shown in figure 1, an embodiment of the present utility model to provide a kind of thermal evaporation for processing membrance concentration liquid dense Compression apparatus, including:
Evaporation tank 1, for carrying out heat exchange between heat smoke and membrance concentration liquid.It is provided with flue gas on the sidewall of evaporation tank 1 Pipe installing hole and liquid-inlet, top is provided with gas outlet 11, and sidewall bottom is provided with liquid outlet.
Heat smoke admission line 2, for providing heat smoke for evaporation tank 1.Heat smoke admission line 2 is through evaporation tank 1 Flue installing hole on sidewall enters evaporation tank 1.Heat smoke admission line 2 is positioned on the tube wall of evaporation tank 1 and is provided with Air-vent, for entering heat smoke in evaporation tank 1.
Membrance concentration liquid enters pipeline 3, for membrance concentration liquid is sent into evaporation tank 1.Membrance concentration liquid enters pipeline 3 through evaporation Liquid-inlet on the sidewall in pond 1 enters evaporation tank 1.Membrance concentration liquid enters pipeline 3 and is positioned at tube wall or the end of evaporation tank 1 On arrange porose, for membrance concentration liquid is entered in evaporation tank 1.
The liquid outlet that the sidewall bottom of discharge line 6, discharge line 6 and evaporation tank 1 is arranged is connected, and is used for discharging film dense Contracting liquid dope.
In this utility model, the heat smoke of use can be the heat smoke that garbage incinerator fire grate goes out.In normal conditions, rubbish The temperature of the heat smoke that rubbish incinerator is discharged is about 240 DEG C, accounts for about the 18% of rubbish gross calorific value, the hot cigarette after deacidification process The temperature of gas is about 190 DEG C, and after bag-type dust, temperature is about 185 DEG C.Owing to deacidification heat smoke before treatment containing NOX、SOX、 HCl, escape ammonia and ash grade, complicated component and have corrosivity, therefore, this utility model be preferably used process through deacidification and Bag-type dust processes the purest heat smoke after removing mentioned component to concentrate for the thermal evaporation of membrance concentration liquid.By Being the purest above-mentioned heat smoke in the heat smoke used, therefore without the concern for the secondary pollution problem of flue gas, film is dense The steam formed after the evaporation of contracting liquid is after heat smoke is together with the cold flue gas formed after heat exchange from gas outlet 11 discharge In the condensed fluid that condensation process obtains, comprise only a small amount of ion and little molecule organic, can as in Water Sproading profit With.Based on this, device of the present utility model can also include condenser (condensing unit), and condenser is connected with gas outlet 11, uses In the mixture of the cold flue gas that the steam and heat smoke that receive the evaporation formation of membrance concentration liquid are formed after heat exchange, and will This mixture cools down so that it is in vaporous water condense out and become aqueous water.
Use that above-described embodiment of the present utility model provides when the thermal evaporation enrichment facility processing membrance concentration liquid, film Concentrated solution enters pipeline 3 from membrance concentration liquid and enters evaporation tank 1, is divided into two-layer, Qi Zhongshang in evaporation tank 1 after staticly settling Layer is membrance concentration liquid clear liquid (upper clear supernate), and lower floor is membrance concentration liquid dope (bottom dope).Heat smoke passes through heat smoke air inlet Pipeline 2 enters in evaporation tank 1, and carries out heat exchange in evaporation tank 1 with membrance concentration liquid clear liquid, thus the heat that heat smoke is carried Membrance concentration liquid clear liquid can be passed to so that the evaporation of membrance concentration liquid clear liquid forms steam, and steam moves upward, and heat smoke warp The cold flue gas formed after crossing heat exchange is discharged from gas outlet 11 together, and membrance concentration liquid dope is then discharged from discharge line 6.Can Seeing, said apparatus can effectively utilize the waste heat of heat smoke to heat concentration membrance concentration liquid clear liquid, both make use of the hot cigarette of waste gas The energy of gas waste heat, decrease water consumption, again by membrance concentration liquid minimizing.
According to one of the present utility model preferred embodiment, the flue sidewall of evaporation tank 1 arranged is installed Hole is higher than liquid-inlet, so that the position of heat smoke admission line 2 enters pipeline 3 higher than membrance concentration liquid, so can subtract Few flue gas disturbance to membrance concentration liquid, reduces crystallization or the attachment (material of crystallization of dope on heat smoke admission line 2 surface Or the dope overwhelming majority is from membrance concentration liquid dope), it is also beneficial to cold flue gas that heat smoke formed after heat exchange and from film The steam being evaporated in concentrated solution is discharged from gas outlet 11.
According to one of the present utility model preferred embodiment, heat smoke admission line 2 passes on the sidewall of evaporation tank 1 Flue installing hole after extend to the offside sidewall of evaporation tank 1, in order to heat smoke and membrance concentration liquid clear liquid are carried out fully Heat exchange.It is further preferred that heat smoke admission line 2 gos deep into the bottom of evaporation tank 1 and/or downside has air-vent, Heat smoke can be sprayed from downside, thus be conducive to and membrance concentration liquid clear liquid carry out heat exchange.Heat smoke admission line 2 Can be one or more, can exert oneself according to evaporation and determine the quantity of heat smoke admission line 2.On smoke inlet pipe road 2 The size of air-vent and spacing can exert oneself according to the flow velocity of heat smoke, flow and evaporation and determine.Wherein, new in this practicality In type, evaporation is exerted oneself and is referred to the speed that membrance concentration liquid clear liquid is evaporated by the evaporability of heat smoke in the unit interval or heat smoke Degree.
According to one of the present utility model preferred embodiment, membrance concentration liquid enters pipeline 3 can be one or more. Many membrance concentration liquid entrance pipelines 3 are set membrance concentration liquid can be sent directly into the diverse location in evaporation tank 1, thus accelerate Processing speed to membrance concentration liquid, improves the work efficiency of device of the present utility model.
According to one of the present utility model preferred embodiment, in order to prevent the bottom alluvial of evaporation tank 1 from causing concentrating Membrance concentration liquid can not discharge smoothly, the liquid outlet that the sidewall bottom of evaporation tank 1 is arranged can be multiple;Each liquid outlet All can connect a discharge line 6, and, some discharge lines 6 are arranged on the sidewall of evaporation tank 1, some discharge pipes The center bottom of road 6 evaporation tank to be extend into 1;Further, each discharge line 6 can also arrange pump, in order to film Concentrated solution dope carries out pump drainage, thus further reduces the generation of the bottom alluvial of evaporation tank 1.
In order to reduce disturbance (meeting when this disturbance is serious that membrance concentration liquid is caused by the heat smoke in evaporation tank 1 further The most layered membrance concentration liquid is made to re-mix into the membrance concentration liquid that concentration is consistent), as it is shown in figure 1, of the present utility model one In planting preferred embodiment, also include anti-disturbance orifice plate 4.Anti-disturbance orifice plate 4 can be a flat board, flat board is provided with many Individual hole.Anti-disturbance orifice plate 4 is arranged on the flue installing hole bottom of evaporation tank 1, such as it is shown in figure 1, support can be passed through (such as steelframe) is supported on sidewall or the bottom of evaporation tank 1.Anti-disturbance orifice plate 4 is set in such a manner, both can make film The top that concentrated solution clear liquid arrives anti-disturbance orifice plate 4 by the hole on anti-disturbance orifice plate 4 carries out heat exchange with heat smoke, enters again one Step reduces the flue gas disturbance to membrance concentration liquid, thus improves treatment effeciency.
In order to make membrance concentration liquid the most static and precipitated and separated, as it is shown in figure 1, the most real in one of the present utility model Execute in mode, also include anti-disturbance distribution grid 5.Anti-disturbance distribution grid 5 can be a flat board, and this flat board can be reinforced concrete Soil structure.Anti-disturbance distribution grid 5 is arranged on membrance concentration liquid and enters below the mouth of pipe of pipeline 3, and the most adjacent membrance concentration liquid enters pipe The mouth of pipe in road 3, distance therebetween can be such as 2mm.It is supported on as it is shown in figure 1, support (such as steelframe) can be passed through The sidewall of evaporation tank 1 or bottom.Anti-disturbance distribution grid 5 is set in such a manner, owing to entering pipeline 3 row from membrance concentration liquid Entering the membrance concentration liquid in evaporation tank 1 and have certain initial velocity, first membrance concentration liquid can be distributed in anti-disturbance after entering evaporation tank 1 On distribution grid 5, thus reduce the kinetic energy of membrance concentration liquid, the most just reduce the membrance concentration liquid newly the entered film to previously having entered dense The disturbance of contracting liquid, decreases the time required for the layering of membrance concentration liquid precipitate.
Preferably, this utility model also includes pre-procesor (not shown), for carrying out preposition to nanofiltration concentrated solution Processing, pre-procesor includes regulating container and humic sorrel extraction system.Wherein, regulation container is used for accommodating nanofiltration concentration Liquid.NaOH is added, for reducing the Ca in nanofiltration concentrated solution in regulation container2+、Mg2+, nanofiltration concentrated solution is in regulation container Layering forms upper clear supernate layer and bottom concentrates liquid layer.Humic sorrel extraction system is used for absorbing upper clear supernate layer.Use above-mentioned Pre-procesor preposition process that nanofiltration concentrated solution is carried out can be: in nanofiltration concentrated solution, first add NaOH, adjust PH value is to 12, and then quiescent setting, to reduce the Ca in nanofiltration concentrated solution2+、Mg2+.PH value is adjusted to arrive the upper clear supernate after precipitation Humic acid film extraction system is entered after 7.Through reducing the Ca in nanofiltration concentrated solution in regulation container2+、Mg2+Process and pass through Nanofiltration concentrated solution after humic sorrel extraction system processes enters processing means of the present utility model.For reverse osmosis concentrated liquid It is made without above-mentioned preposition process, evaporation tank 1 can be sent directly into and process.
As it is shown in figure 1, specific works process of the present utility model is described in detail as a example by nanofiltration concentrated solution below:
First nanofiltration concentrated solution carried out preposition process before entering evaporation tank 1, and processing procedure is as follows:
First adding NaOH in nanofiltration concentrated solution, adjust pH value to 12, then quiescent setting, to reduce in nanofiltration concentrated solution Ca2+、Mg2+.PH value is adjusted to enter humic acid film extraction system after 7 the upper clear supernate after precipitation.Pass through in regulation container Reduce the Ca in nanofiltration concentrated solution2+、Mg2+Process and the nanofiltration concentrated solution after humic sorrel extraction system processes are Above-mentioned membrance concentration liquid, by this membrance concentration liquid with the thermal evaporation concentration device for processing membrance concentration liquid of the present utility model The process carrying out processing is as follows:
Above-mentioned membrance concentration liquid is entered pipeline 3 from membrance concentration liquid and enters evaporation tank 1, owing to membrance concentration liquid enters pipeline 3 Having anti-disturbance distribution grid 5 (the two is at a distance of 2mm) below the mouth of pipe, first membrance concentration liquid can be distributed on anti-disturbance distribution grid 5, from And reduce the kinetic energy of membrance concentration liquid.Enter pipeline 3 by membrance concentration liquid and enter the membrance concentration liquid of evaporation tank 1, stand, Under gravity, membrance concentration liquid is divided into the membrance concentration liquid supernatant layer (upper clear supernate layer) on upper strata and lower floor in evaporation tank 1 Membrance concentration liquid dope layer (bottom dope layer), when upper clear supernate is near heat smoke admission line 2 (such as close to anti-disturbance orifice plate When 4) or submergence heat smoke admission line 2 after (now should stop input membrance concentration liquid), be passed through in thermotropism smoke inlet pipe road 2 Pure heat smoke after deacidification process and bag-type dust process, heat smoke is from the tube wall of heat smoke admission line 2 The air-vent arranged enters in membrance concentration liquid clear liquid, and carries out heat exchange with membrance concentration liquid clear liquid, thus is added by membrance concentration liquid clear liquid Thermal evaporation produce steam, steam moves upward, with heat smoke through after heat exchange formed cold flue gas together with from giving vent to anger Mouth 11 is discharged, and the membrance concentration liquid dope being deposited on lower floor after standing is then discharged (opening for pump drainage if desired from discharge line 6 The pump of portion's dope).The mixture of the cold flue gas that steam and heat smoke are formed after heat exchange can be cold by condenser But, vaporous water therein condenses out and becomes aqueous water, and aqueous water can collect and use as middle water.Owing to being arranged on steaming Send out the existence of the anti-disturbance orifice plate 4 of the flue installing hole bottom in pond 1, be possible not only to make membrance concentration liquid clear liquid through anti-disturbance Orifice plate 4 and heat smoke carry out sufficient heat exchange, and can greatly reduce heat smoke disturbing the most layered membrance concentration liquid Dynamic.
Above-mentioned preposition process is made without for reverse osmosis concentrated liquid, evaporation tank 1 can be sent directly into and process.
From foregoing, the thermal evaporation enrichment facility being used for processing membrance concentration liquid of this utility model offer can be adopted Directly membrance concentration liquid heating evaporation is concentrated, i.e. heat smoke with discarded heat smoke (heat smoke that such as incinerator is discharged) Through direct heat transfer, heat energy is forwarded to membrance concentration liquid, membrance concentration liquid evaporation and concentration is formed membrance concentration liquid dope and steam, And the membrance concentration liquid of steam and concentration separately can be processed, steam can also recycle, and membrance concentration liquid can be by Fully concentrating, therefore this utility model can make full use of discarded smoke discharging residual heat, had both decreased energy resource consumption, and had reclaimed preciousness Water resource, make again membrance concentration liquid minimizing.
The air-vent on heat smoke admission line 2 that this utility model is arranged is so that between heat smoke and membrance concentration liquid Sufficient heat exchange can be carried out, improve the utilization rate of the energy.
This utility model, can the disturbance that causes membrance concentration liquid of the most less heat smoke by arranging anti-disturbance orifice plate 4.
This utility model membrance concentration by arranging anti-disturbance distribution grid 5, after membrance concentration liquid can being greatly reduced and concentrating Disturbance between liquid, it is ensured that the concentrated effect good to membrance concentration liquid.
As known by the technical knowledge, this utility model can be by other essence without departing from its spirit or the reality of essential feature The scheme of executing realizes.Therefore, embodiment disclosed above, for each side, all it is merely illustrative, is not only 's.All in the range of this utility model or be equal to the change in the range of this utility model all by this utility model bag Contain.

Claims (10)

1. the thermal evaporation enrichment facility being used for processing membrance concentration liquid, it is characterised in that including:
Evaporation tank, the sidewall of described evaporation tank is provided with flue installing hole and liquid-inlet, and top is provided with gas outlet, Sidewall bottom is provided with liquid outlet;
Heat smoke admission line, described heat smoke admission line enters through the flue installing hole on the sidewall of described evaporation tank Entering described evaporation tank, described heat smoke admission line is positioned on the tube wall of described evaporation tank and is provided with air-vent, for by heat Flue gas enters in described evaporation tank;
Membrance concentration liquid enters pipeline, and described membrance concentration liquid enters pipeline and enters through the liquid-inlet on the sidewall of described evaporation tank Described evaporation tank, described membrance concentration liquid enter pipeline be positioned at arrange on the tube wall of described evaporation tank porose, for by membrance concentration Liquid enters in described evaporation tank;
The liquid outlet that the sidewall bottom of discharge line, described discharge line and described evaporation tank is arranged is connected, and is used for discharging film Concentrated solution dope.
Thermal evaporation enrichment facility for processing membrance concentration liquid the most according to claim 1, it is characterised in that described evaporation The flue installing hole arranged on the sidewall in pond is higher than liquid-inlet, so that the position of described heat smoke admission line is high Pipeline is entered in described membrance concentration liquid.
Thermal evaporation enrichment facility for processing membrance concentration liquid the most according to claim 1, it is characterised in that described hot cigarette Gas admission line extends to the offside sidewall of described evaporation tank after passing the flue installing hole on the sidewall of described evaporation tank.
Thermal evaporation enrichment facility for processing membrance concentration liquid the most according to claim 3, it is characterised in that described hot cigarette Gas admission line gos deep into the bottom of described evaporation tank and/or downside has air-vent so that heat smoke is from bottom and/or downside Face sprays.
Thermal evaporation enrichment facility for processing membrance concentration liquid the most according to claim 4, it is characterised in that described hot cigarette Gas admission line is one or more;
It is one or more that described membrance concentration liquid enters pipeline;
The liquid outlet that the sidewall bottom of described evaporation tank is arranged is multiple, and each described liquid outlet is all connected with a discharge pipe Road;
Each described discharge line is additionally provided with pump, in order to the membrance concentration liquid after concentrating is carried out pump drainage.
Thermal evaporation enrichment facility for processing membrance concentration liquid the most according to claim 1, it is characterised in that also include:
Anti-disturbance orifice plate, described anti-disturbance orifice plate is arranged on the flue installing hole bottom of described evaporation tank, described anti-disturbance Orifice plate is flat board, and flat board is provided with multiple hole.
7. according to the thermal evaporation enrichment facility for processing membrance concentration liquid described in claim 1 or 6, it is characterised in that also wrap Include:
Anti-disturbance distribution grid, described anti-disturbance distribution grid is arranged on described membrance concentration liquid and enters below the mouth of pipe of pipeline.
Thermal evaporation enrichment facility for processing membrance concentration liquid the most according to claim 7, it is characterised in that described interference guard Dynamic distribution grid is flat board, and described anti-disturbance distribution grid enters the mouth of pipe 2mm of pipeline apart from described membrance concentration liquid.
Thermal evaporation enrichment facility for processing membrance concentration liquid the most according to claim 1, it is characterised in that also include:
Condenser, described condenser is connected with described gas outlet, for receiving steam and the hot cigarette that the evaporation of membrance concentration liquid is formed The mixture of the cold flue gas that gas is formed after heat exchange, and this mixture is cooled down so that it is in vaporous water condensation become Aqueous water.
Thermal evaporation enrichment facility for processing membrance concentration liquid the most according to claim 1, it is characterised in that described film Concentrated solution includes nanofiltration concentrated solution and reverse osmosis concentrated liquid, and when described membrance concentration liquid is nanofiltration concentrated solution, described device also wraps Include:
Pre-procesor, for carrying out preposition process to nanofiltration concentrated solution;Described pre-procesor includes:
Regulation container, is used for accommodating nanofiltration concentrated solution, adds NaOH, be used for reducing in nanofiltration concentrated solution in described regulation container Ca2+、Mg2+, nanofiltration concentrated solution be layered in described regulation container formation upper clear supernate layer and bottom concentrate liquid layer, described under Portion concentrates liquid layer and enters described heat exchanger;With
Humic sorrel extraction system, is used for absorbing described upper clear supernate layer.
CN201620744884.6U 2016-07-14 2016-07-14 A kind of thermal evaporation enrichment facility for processing membrance concentration liquid Expired - Fee Related CN205838604U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201620744884.6U CN205838604U (en) 2016-07-14 2016-07-14 A kind of thermal evaporation enrichment facility for processing membrance concentration liquid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201620744884.6U CN205838604U (en) 2016-07-14 2016-07-14 A kind of thermal evaporation enrichment facility for processing membrance concentration liquid

Publications (1)

Publication Number Publication Date
CN205838604U true CN205838604U (en) 2016-12-28

Family

ID=57619519

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201620744884.6U Expired - Fee Related CN205838604U (en) 2016-07-14 2016-07-14 A kind of thermal evaporation enrichment facility for processing membrance concentration liquid

Country Status (1)

Country Link
CN (1) CN205838604U (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106186127A (en) * 2016-07-14 2016-12-07 中国城市建设研究院有限公司 A kind of thermal evaporation enrichment facility for processing membrance concentration liquid

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106186127A (en) * 2016-07-14 2016-12-07 中国城市建设研究院有限公司 A kind of thermal evaporation enrichment facility for processing membrance concentration liquid
CN106186127B (en) * 2016-07-14 2022-08-26 中国城市建设研究院有限公司 Thermal evaporation concentration device for treating membrane concentrated solution

Similar Documents

Publication Publication Date Title
CN207525092U (en) A kind of garbage percolation liquid treating system and refuse disposal system
CN103524005B (en) Combined type environment-friendly device using MVR-bipolar electrolysis-biological enhancement technology
CN1298640C (en) Resource process of inflitration liquid
CN103848464B (en) The treatment process of low-temperature evaporation high-concentration sewage
CN109987780A (en) Garbage percolation liquid treating system and its technique based on sewage source heat pump technology
CN103848463A (en) Treatment device of low-temperature evaporation high-concentration sewage
CN201793398U (en) Household garbage leachate harmless treatment device
CN205838604U (en) A kind of thermal evaporation enrichment facility for processing membrance concentration liquid
CN203820489U (en) Low-temperature evaporation treatment device for high-concentration wastewater
CN211198958U (en) Garbage leachate low-energy-consumption full-quantification treatment system
CN112225275A (en) Contain high-efficient evaporation plant of salt organic waste water and system
CN103723901A (en) Method for preheating digestion treatment inlet sludge by sludge drying waste heat
CN211367298U (en) Novel system for treating industrial wastewater by using bypass low-temperature flue gas
CN101774747B (en) Device for performing reduction treatment on drilling waste water by using diesel exhaust and treatment method thereof
CN206051603U (en) A kind of thermal evaporation concentration systems of membrance concentration liquid
CN106186127A (en) A kind of thermal evaporation enrichment facility for processing membrance concentration liquid
CN106587238A (en) Sea water desalination system and method with low temperature exhaust heat utilization function
CN105601016A (en) Chemical nickel waste liquid integrated processing system
CN110963623A (en) Novel system for treating industrial wastewater by using bypass low-temperature flue gas
CN214192637U (en) Contain high-efficient evaporation plant of salt organic waste water and system
CN207958073U (en) Waste incineration percolation liquid treating system
CN104108760B (en) A kind for the treatment of unit of oily(waste)water and treatment process thereof
CN205838605U (en) A kind of thermal evaporation concentration device of membrance concentration liquid
CN201634463U (en) Device for minimizing drilling wastewater by utilizing diesel exhaust
CN203568941U (en) Combined environment-friendly equipment adopting MVR (Mechanical Bapor Recompression)-bipolar electrolysis-bioaugmentation technology

Legal Events

Date Code Title Description
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20161228

CF01 Termination of patent right due to non-payment of annual fee