CN1262236A - Desulfurization waste water treating method - Google Patents
Desulfurization waste water treating method Download PDFInfo
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- CN1262236A CN1262236A CN 99101283 CN99101283A CN1262236A CN 1262236 A CN1262236 A CN 1262236A CN 99101283 CN99101283 CN 99101283 CN 99101283 A CN99101283 A CN 99101283A CN 1262236 A CN1262236 A CN 1262236A
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Abstract
A process for treating the waste water generated by desulfurizing fume includes evaporizing the waste liquid to decrease its volume and mixing with solidifying agent to become solid matter. A solid-liquid separator is used to separate out gypsum for recovery. The part or all of recovered gypsum is added into evaporator or to the waste water in evaporator. Its rest is discharged or returned back to desulfurizing equipment for recovering gypsum. The vapour in condensing evaporator is used as condensed liquid to flush evaporator regularly.
Description
The present invention relates to the waste water thickening treatment process of FGD system discharging; consider that from the viewpoint of environment protection this system is suitable for by using alkaline reagents (as Wingdale) to make existing oxysulfide gas (to call " SOx gas " in the following text) in absorption agent absorption and the segregated combustion waste gas.In this manual, such waste water abbreviates " waste water " as.
2. description of related art
Waste water contains main component such as calcium chloride, magnesium chloride and dissolved gypsum, submember comprises solid matter, as the combust that exists in the combustion exhaust with because the gypsum that reaction forms, the dissolved metal ingredient, and formed nitrogen-sulphur compound (hereinafter being called " N-S compound ") in the flue gas desulfurization process, like that.Therefore, in fact such waste water can not be discharged into the public waters, must be through handling to satisfy the emission standard of law defined.
Recently, in order to reduce the floor space of processing costs and treatment unit, it is promising that following method has been considered to.Comprise that in these class methods waste water evaporates the method for handling again behind its volume to reduce in vaporizer, and waste water evaporation is earlier passed through to add auxiliary curing agent solidified method again to reduce its volume.In these treatment processs, metal ingredient and chemical oxygen demand (COD) composition are all processed.Therefore, with regard to equipment size, occupation area of equipment and operation control, compare with the conventional treatment method that waste water is handled respectively according to the component type that will remove, aforesaid method is very favorable.
Fig. 8 is the schema that the conventional processing system example of vaporizer and solidification equipment is equipped with in explanation, and corresponding treatment process process is described hereinafter with reference to this figure.
In Fig. 8, be stored in the storage tank 101 and enrichment by evaporation in vaporizer 102 from the waste water of FGD system (not shown).Waste water in well heater 103 heating fumigators 102 is to replenish the heat that is lost because of the waste water evaporation, the waste water that storage tank 104 stores with vaporizer 102 enrichments.The steam that produces in condenser 105 condenser/evaporators 102 also reclaims as phlegma, and kneading machine 106 is kneaded the waste water of enrichment with the formation solid matter with auxiliary curing agent.Premixer 107 is used to be pre-mixed the auxiliary curing agent (for example coal ash and cement) that is used to solidify enrichment waste water.Pump 108 is used for the waste water in the storage tank 101 is delivered in the vaporizer 102, and pump 109 is used for the enrichment waste water of storage tank 104 is delivered in the kneading machine 106.Air extractor 110 be used for carrying steam that vaporizer 102 produced to condenser 105 and the relief condenser 105 any incondensable gas to the system outside.
Waste water from the desulphurization system (not shown) is introduced storage tank 101 through pipeline aa, in this storage, delivers to 102 li in vaporizer through line c c and pump 108 then.
In addition, in order to prevent that institute's dissolved gypsum is owing to waste water deposition that enrichment causes in vaporizer 102 and formation fouling in the waste water, and cause the decline of heat transfer property thus and cause the difficulty of enrichment waste water thus, will add to storage tank 101 through line b b as the gypsum of crystal seed.
In vaporizer 102, waste water is through evaporation and by enrichment and be divided into the waste water and the steam of enrichment.Usually, in order to promote the evaporation in vaporizer 102, waste water heats by heating medium such as steam, the vaporizer 102 of finding time simultaneously.Waste water is to be discharged by vaporizer 102 and heat in well heater 103 and turn back to vaporizer 102 again through pipeline dd.On the other hand, supply heating mediums through pipeline ff to well heater 103, to be used for carrying out heat exchange, again outside pipeline ff ' discharge system with waste water.
Deliver to storage tank 104 via pipeline dd waste water (being the waste water of enrichment) by evaporation enrichment in vaporizer 102.Then, the enrichment waste water from storage tank 104 is delivered to kneading machine 106 by pump 109 through pipeline ii.In this process, adding is contained in the waste water of enrichment as the gypsum of crystal seed and with sedimentary gypsum in vaporizer 102 in the storage tank 104, delivers to storage tank 104 through pipeline dd again.
The steam that produces in the vaporizer 102 transfers to condenser 105 by air extractor 110 through pipeline ee.Cooling steam and condensation in condenser 105, resulting phlegma is discharged and is reclaimed through pipeline gg.The phlegma that reclaims reuses by the make-up water of its quality as boiler or desulphurization system.Any incondensable gas in the condenser 105 all will be discharged system by pipeline nn by air extractor 110.In addition, the cold water that is used for cooling steam feeds to condenser 105 and by pipeline hh ' discharge system through pipeline hh.
The coal ash and the cement that use as auxiliary curing agent to premixer 107 feed through pipeline jj and kk, and do not knead so that do not influence in this mixing.Mixed auxiliary curing agent transfers to kneading machine 106 and kneads and form solid matter at this with the enrichment waste water of sending into through pipeline ii through pipeline pp in premixer 107.This solid matter discharges from kneading machine 107 through pipeline mm.Usually, this solid matter is disposed as industrial waste.
Summary of the invention
In the wastewater treatment of routine, must in storage tank, add the crystal seed gypsum so that minimum is reduced in the gypsum formed fouling in vaporizer and well heater that causes because of the waste water enrichment.This point requires to use the crystal seed feeder of constant speed, and has also increased the solids quality of discharging from kneading machine, i.e. refuse amount.
If do not add gypsum seed, then in vaporizer and well heater, will form fouling.This can cause the decline of heat transfer coefficient and make the impossible enrichment of waste water.
The object of the present invention is to provide a kind of method that addresses these problems.
According to the first embodiment of the present invention, provide a kind of treatment process that is used for desulfurization wastewater, the step that this method comprises has: in the vent line of vaporizer discharging enrichment waste water a solid-liquid separator that is used to separate gypsum is installed; Gypsum in separation and the recovery enrichment waste water; The gypsum of all or part of recovery is added to vaporizer or delivers in the waste water of vaporizer and be disposed to the recovery gypsum of any remainder outside the system or it is returned desulfurizer so that the gypsum that can form reclaims in desulfurizer.
According to second embodiment of the invention, a kind of treatment process of desulfurization wastewater is provided, be added in the above-mentioned vaporizer after all or part of gypsum that wherein will reclaim in above-mentioned solid-liquid separator is pulverized or be added in the waste water of sending into above-mentioned vaporizer.
According to the 3rd embodiment of the present invention, a kind of treatment process of desulfurization wastewater is provided, this method is not added to vaporizer to the crystal seed gypsum or is added in the waste water of delivering in this vaporizer, but comprises following step: the steam that produces in the condenser/evaporator is to reclaim as phlegma; And periodically wash vaporizer with the phlegma that reclaims.
According to the 4th embodiment of the present invention, a kind of treatment process of desulfurization wastewater is provided, wherein first or second embodiment and the 3rd embodiment are combined and carry out.
Thereby might reduce to minimum level to formed gyrpseous scale in the waste water enrichment step according to desulfurization wastewater treatment process of the present invention makes wastewater treatment process stably move long time.In addition, owing to the gypsum that reclaims can reuse as crystal seed, so there is no need outside system, to supply gypsum.This point has been eliminated the necessity of using constant speed crystal seed gypsum feeder.And, separates and reclaims owing to will be present in by the gypsum in the enrichment degree water of vaporizer discharging, so that the solids quality minimizing of discharging in the kneading machine.In addition, the formation of fouling is reduced to greatest extent owing to adding crystal seed gypsum or owing to washing vaporizer with the phlegma that reclaims in the condenser in vaporizer and the well heater.
Fig. 1 is the schema that shows an embodiment, and wherein, all or part of gypsum that the enrichment waste water of being discharged by the solid-liquid separating evaporator reclaims reuses as crystal seed;
Fig. 2 shows identically with Fig. 1 embodiment, and just to separate be embodiment schema by using single clarifying tank to finish to solid-liquid;
Fig. 3 shows identically with Fig. 1 embodiment, just pulverizes by the gypsum of solid-liquid Separation and Recovery and is added to embodiment schema in the waste water of delivering to vaporizer;
Fig. 4 shows identically with Fig. 2 embodiment, just pulverizes by the gypsum of solid-liquid Separation and Recovery and is added to embodiment schema in the waste water of delivering to vaporizer;
Fig. 5 shows that the phlegma that reclaims is used to the embodiment schema that sedimentary vaporizer of gyrpseous scale and well heater easily take place in periodically flushing in condenser;
Fig. 6 be show with Fig. 1 embodiment quite and the phlegma that wherein in condenser, reclaims be used to periodically flushing sedimentary vaporizer of gyrpseous scale and well heater easily take place, and separate the embodiment schema that all or part of gypsum that the enrichment waste water of being discharged by vaporizer reclaims reuses as crystal seed by solid-liquid;
Fig. 7 be show identical with Fig. 6 embodiment, just through improving so that the embodiment schema suitable with Fig. 2 embodiment; With
Fig. 8 is the embodiment schema that shows the conventional Waste Water Treatment that vaporizer and solidification equipment are installed.
The present invention relates to a kind of processing method of the desulfurization wastewater that from FGD system, discharges, This desulphurization system is suitable for by using alkaline reagent to make absorbent by absorbing in the burnt gas and removal sulphur Oxide gas.
In the method, make earlier by the waste water that discharges in the FGD system in evaporimeter, evaporate with Reduce its volume and knead to form solid matter with auxiliary curing agent then. According to of the present invention first Embodiment, this method comprise the steps: in the discharge pipe line of evaporimeter discharging enrichment waste water Solid-liquid separator for separating of gypsum is installed; In solid-liquid separator by in the enrichment waste water Separate and the recovery gypsum; Join all or part of recovery gypsum in the waste water that is sent to evaporimeter and the general The recovery gypsum of any arrear is discharged system or it is turned back to desulfurizer in order to can fill with desulfurization Putting interior formed gypsum reclaims together.
Be used for solid-liquid separator of the present invention and can comprise single solid-liquid separator or two kinds of different consolidating The separator of-liquid/gas separator combination. The necessity of more particularly, separating according to solid-liquid can be used Such as defecator, the separator that liquid cyclone and whizzer are such.
Available auxiliary curing agent comprises coal ash, cement etc. These auxiliary curing agents can use separately also and can organize Close use. The type of used auxiliary curing agent and quantity will have requirement property in order to can form through selecting The solid matter of energy (for example compression strength and solubility).
In improved embodiment, all or partially recycled gypsum can directly be added in the evaporimeter, Rather than it is added in the waste water that is sent to evaporimeter.
According to first embodiment of the present invention, formed gypsum can pass through solid-liquid in evaporimeter Separate and reclaim, and all or part of gypsum that reclaims can be used as the crystal seed in the evaporimeter. This Point has in the equipment such as can making heater formed gyrpseous scale and is down to minimum degree, and reduces and introduce Thereby the amount of gypsum of kneader reduces many advantages of the solids quality that forms in the kneading machine. This There is no need outside system, to supply gypsum outward. So just eliminated the necessity of using the constant speed feeder. And, can use various combination solid-liquid separator (examples for separating of the gypsum that forms in the evaporimeter As, be used for the combination of the liquid cyclone of first embodiment and defecator and be used for the second enforcement side The defecator of case) to reach the fully separation of gypsum. In addition, this is also advantageous in that the stone of separating Cream can reclaim to reuse or be used for other purposes.
First embodiment of the present invention is described as specific embodiment below by the treatment process of taking to be shown among Fig. 1 and Fig. 2.In the method or system in being shown in Fig. 1-8, indicate same unit with same reference symbol.In Fig. 8, the unit of indicating with three-figure numeral is identical with shown in Fig. 1-the 7 and unit of indicating with the same numbers that deducts 100 basically.Among Fig. 8, the unit of indicating with biliteral is identical with shown in Fig. 1-the 7 and unit of indicating with corresponding single-letter basically.Fig. 1 shows the embodiment that two kinds of solid-liquid separators are installed in series, and Fig. 2 shows the embodiment that single solid-liquid separator is installed.
Fig. 1 shows by solid-liquid to separate all or part of gypsum that the enrichment waste water of being discharged by vaporizer 2 reclaims again as the embodiment schema of crystal seed.
In Fig. 1, the waste water that storage tank 1 stores from the FGD system (not shown), and vaporizer 2 is by evaporation enrichment waste water.Waste water in well heater 3 heating fumigators 2 is to replenish the heat that loses because of its evaporation, the waste water that storage tank 4 stores by vaporizer 2 enrichments.The steam that is produced in condenser 5 condenser/evaporators 2 is to reclaim it and kneading machine 6 is kneaded enrichment waste water and auxiliary curing agent to form solid matter as phlegma.Premixer 7 is used for being pre-mixed the auxiliary curing agent (for example coal ash and cement) that is used to solidify enrichment waste water.Pump 8 is used for the waste water of storage tank 1 is sent into vaporizer 2, and pump 9 is used for the enrichment degree water of storage tank 4 is sent into kneading machine 6.Air extractor 10 is used for the steam that vaporizer 2 produces is transferred to the outside that condenser also is discharged to any incondensable gas in the condenser 5 system.Storage tank 4 be isolated and be imported to liquid cyclone 11 can from the gypsum that vaporizer 2 is discharged the enrichment waste water haply., clarifying tank 12 further gathers with liquid cyclone 11 isolating gypsum.
In Fig. 1, the waste water from the desulphurization system (not shown) is introduced storage tank 1 through pipeline a, and be stored in wherein, deliver in the vaporizer 2 by line c and pump 8 then.
In vaporizer 2, waste water is by the evaporation enrichment and be separated into enrichment waste water and steam, in order to promote the evaporation in the vaporizer 2, makes waste water by means of heating medium such as steam heating, and simultaneously vaporizer 2 is found time.Waste water heats from vaporizer 2 dischargings by pipeline d, with well heater 3 heating, and then turns back to vaporizer 2.On the other hand, supply the heating medium that comprises low-pressure steam to well heater 3, be used for heated waste water, then through pipeline f ' discharge system through pipeline f.
The steam that produces in the vaporizer 2 is recovered as the phlegma of condenser 5 and discharges system through pipeline g.Use the heat-eliminating medium of water coolant as condenser 5.By any incondensable gas and the discharge system in the vacuum pump 10 extraction condensers 5.
In vaporizer 2 (being enrichment waste water) evaporation and the waste water of enrichment is sent in the liquid cyclone 11 through pipeline g.In enrichment waste water, concentrate the dissolved gypsum to hypersaturated state and as solid precipitation.Form fouling in order to prevent gypsum to be deposited on the surface in contact of vaporizer 2 and well heater 3, the gypsum (as mentioned below) that reclaims in clarifying tank 12 is introduced also be used as crystal seed in the waste water that is sent in the vaporizer 2.
In liquid cyclone 11, the gypsum that will be present in the enrichment waste water is separated from liquid component by centrifugal force, determines its dimensions (for example particle diameter of Shou Jiing) by the gypsum particle diameter that measurement collection arrives.To deliver to storage tank 4 through pipeline r at the enrichment degree water that liquid cyclone 11 separates gypsum.On the other hand, the gypsum of collecting at liquid cyclone 11 is delivered in the clarifying tank 12 via pipeline s, and sedimentation therein is so that further improve the concentration of gypsum.
Through pipeline t discharging, its all or part of pipeline u that stimulates the menstrual flow is added to the waste line c that is used for reinforced waste water and sends into vaporizer 2 with the high density gypsum in the clarifying tank 12.Its any remainder all can be via pipeline v the discharge system.
Gypsum add-on as crystal seed can be determined by sedimentary amount of gypsum, and precipitation capacity depends on the enrichment condition and the liquid property of waste water in the vaporizer.
The liquid that has separated gypsum at clarifying tank 12 (being supernatant liquid) is delivered in the storage tank 4 through pipeline w.Again the enrichment waste water in the storage tank 4 is sent in the kneading machine 6 through pump 9 and pipeline i, then with in premixer 7, mixing and kneading and form solid matter by the auxiliary curing agent of premixer supply.
Will the treatment process that be shown among Fig. 2 be described below.
Fig. 2 be show with separate by solid-liquid that all or part of gypsum that the enrichment waste water of being discharged by vaporizer 2 reclaims reuses as crystal seed and also solid-liquid to separate be embodiment schema by using single clarifying tank 12 to implement.
Part enrichment waste water in the vaporizer 2 is sent to 12 li of clarifying tanks through pipeline q, and gypsum gathers by deposition.The gypsum that gathers is discharged by pipeline t, and it all or part ofly is added among the charge line c of vaporizer 2 through pipeline u.Any residual part gypsum is all through pipeline v and the discharge system.Having separated the liquid (being supernatant liquid) of gypsum in clarifying tank 12 sends in the storage tank 4 via pipeline w.
In desulfurization wastewater treatment process, after pulverizing, all or part of gypsum that reclaims in the solid-liquid separator is added in the waste water of delivering to vaporizer according to second embodiment of the invention.
According to second embodiment, by the solid-liquid Separation and Recovery in vaporizer formed gypsum and with all or part of recovery gypsum as the crystal seed of vaporizer.So just can reduce in well heater and the device like that formed gyrpseous scale to minimum level, thereby and can reduce the amount of gypsum that enters kneading machine and reduce formed solids quality in the kneading machine.In addition, there is no need outside supply gypsum from system.So just eliminated the necessity of using the constant speed feeder.And separating the gypsum reclaims by solid-liquid will be through pulverizing to reduce its particle diameter, and causing the gypsum surface of unit weight to be amassed has been increased thereby improved the effect of gypsum as crystal seed.In addition, in the recyclable solid-liquid separator the isolating gypsum of institute to reuse or to be used for other purpose.
Crusher or allied equipment can be used for pulverizing gypsum.Although the crusher type is not particularly limited, spendable type comprises stamp mill, wet grinding machine etc.Broken gypsum is more effective with the decline of its median size.Yet in fact its median size should control in the scope of 30-50 μ m, and it is long-pending might to keep or improve the unit weight surface of seed like this.
Perhaps, all or part gypsum that will reclaim in the solid-liquid separator can be pulverized and directly be added in the vaporizer with crusher, rather than it is added in the waste water of sending into vaporizer.
As specific embodiment second embodiment of the present invention is described hereinafter by the treatment process of taking to be shown in Fig. 3 and 4.
Fig. 3 and 4 show respectively by solid-liquid separate that all or part of gypsum that the enrichment waste water of being discharged by vaporizer 2 reclaims reuses as crystal seed and gypsum by the solid-liquid Separation and Recovery with crusher 13 pulverizing and be added to embodiment schema in the waste water of sending vaporizer 2 to.In these figure, x indicates the pipeline that leads to pulverizer 13.
The steam that comprises in the condenser/evaporator being produced according to the treatment process of the desulfurization wastewater of third embodiment of the invention is so that with its step that reclaims as phlegma, and the step of periodically washing vaporizer with the phlegma of recovery.
The equipment that uses the recovery phlegma periodically to wash is not limited to vaporizer, can comprise being easy to take place sedimentary well heater of gyrpseous scale and other parts.
According to third embodiment of the invention, the gyrpseous scale that is generated in well heater etc. can be by using the phlegma that reclaims at condenser and with its dissolving and removal, causing the formation of gyrpseous scale can be reduced to minimum degree.In addition, there is no need outside supply gypsum from system.This point can be eliminated the necessity of using the constant speed feeder.
Washing time is controlled according to sedimentary amount of gypsum in vaporizer.
The treating processes that is shown in Fig. 5 by employing is described the 3rd embodiment of the present invention hereinafter as specific embodiment.
Fig. 5 shows the phlegma that reclaims at condenser 5 is used for the embodiment schema that sedimentary vaporizer 2 of gyrpseous scale and well heater 3 easily take place in periodically flushing.
The condensate stream that reclaims in the condenser 5 is through pipeline g, and temporarily is stored in the holder 14, and it periodically infeeds vaporizer 2 by pump 15 and pipeline y, and through vaporizer 2 and well heater 3 circulations to rinse out sedimentary gyrpseous scale.Before the flushing, the enrichment waste water that wash in the parts escapes and enter storage tank 4 through pipeline d.
Washing fluid returns storage tank 1 through pipeline z.
In the storage tank 14 any remaining recovery phlegmas by pump 16 through pipeline 1 (e1) and the discharge system.
The method that is used for the processing of four embodiment of the invention desulfurization wastewater comprises the steps: at the vent line that is used for by vaporizer discharge enrichment waste water the solid-liquid separator that a separation gypsum is used to be installed; Gypsum in the solid-liquid separator in separation and the recovery enrichment waste water; All or part of gypsum that maybe will reclaim or after pulverizing with crusher is added to vaporizer or is added in the waste water of sending in the vaporizer; The recovery gypsum of any lingering section is discharged system or it is turned back to desulfurizer so that formed gypsum reclaims in desulfurizer; The steam that is produced in the condenser/evaporator reclaims as phlegma; And use the phlegma that reclaims to be easy to take place the sedimentary parts of gyrpseous scale periodically to wash, as vaporizer and/or well heater.
The present invention also comprises improved embodiment, wherein in order further to reduce the deposition of gyrpseous scale, pulverizes with crusher and to be collected at the gypsum in the clarifying tank and to be added in the waste water of sending into vaporizer.
According to four embodiment of the invention, separate by solid-liquid and to reclaim formed gypsum in the vaporizer, and the gypsum of all or part of recovery is used for vaporizer as crystal seed, so that make the gyrpseous scale deposition in well heater etc. can reduce to minimum.Even the formation gyrpseous scale, this gyrpseous scale dissolves periodically by using the phlegma that reclaims in the condenser and removes.Therefore, the formation of gyrpseous scale can be prevented from fully.In addition, there is no need to supply gypsum from the outside of system.This has just been avoided using the necessity of constant speed feeder.And, can also reduce the amount of solid of discharging in the kneading machine.
The 4th embodiment of the present invention is described as specific embodiment below by the treatment process process of taking to be shown in Fig. 6 and 7.
Fig. 6 and 7 is the schemas that show following embodiment respectively, the phlegma that wherein uses condenser 5 to reclaim periodically washes and is easy to take place sedimentary vaporizer 2 of gyrpseous scale and well heater 3, and all or part of gypsum that reclaims with the enrichment waste water that separates by solid-liquid by vaporizer 2 discharges reuses as crystal seed.
In the embodiment that Fig. 6 shows, be connected in series liquid cyclone 1 and clarifying tank 12 as the solid-liquid separator being used for separating the gypsum of the enrichment waste water of discharging by vaporizer 2, and Fig. 7 shows the embodiment of only using clarifying tank 12.
The technical requirements of liquid cyclone and clarifying tank is by determining with the described same procedure of relevant Fig. 1 embodiment.
In order to prove effect of the present invention, the system of scale experimentizes in the middle of adopting.Embodiment 1
Experimentize according to the treatment process that is shown among Fig. 1.Be supplied with 1kg/cm through pipeline f toward well heater 3
2.G the heating medium of low-pressure steam pressure or following.As for the type of well heater 3, can use the interchanger of overcoat and pipe (shell and tube) pattern.
Pressure in the vaporizer 2 is 70mmHg (definitely), and the enrichment wastewater temperature at the entrance and exit place of well heater 3 is respectively 64 ℃ and 67 ℃.Waste water enrichment ratio in the vaporizer 2 is 7.
Should determine that as the amount of gypsum that crystal seed adds this amount is decided according to the enrichment condition and the liquid property of waste water in the vaporizer according to sedimentary amount of gypsum.In this example, control add amount of gypsum so that can be 0.47wt.% in the gypsum concentration in delivering to the waste water of vaporizer.
In this example, coal ash and cement are as auxiliary curing agent.As for their ratio of mixture, based on enrichment waste water, cement uses with the amount of 20wt.% coal ash with the equivalent use.
With gypsum isolating situation from enrichment degree water is not compared, in this example, the solids quality reduces about 16wt.%.Embodiment 2
Experimentize based on treatment process shown in Figure 2.Operational condition is identical with embodiment 1.Embodiment 3
Experimentize based on treatment process shown in Figure 3.Embodiment 3 is identical with embodiment 1, just uses crusher 13 in addition.Stamp mill can be used as crusher 13, and its operational condition will be controlled so that make the gypsum of pulverizing have the median size of 30-50 μ m.Embodiment 4
Experimentize based on treatment process shown in Figure 4.Embodiment 4 is identical with embodiment 2, just uses crusher in addition.The type of crusher is identical with particle diameter of being controlled and embodiment's 3.Embodiment 5
Experimentize based on treatment process shown in Figure 5.Washing time should be according to the amount of gypsum that is settled out in the vaporizer 2.In the present embodiment, washing time be per three days once.Identical among other operational condition of vaporizer 2, kneading machine 6 etc. and the embodiment 1.Embodiment 6
Experimentize based on method shown in Figure 6.The technical requirements of liquid cyclone and clarifying tank is determined by the described same procedure of relevant Fig. 1 embodiment.With the number of times of the phlegma flushing of reclaiming be per ten days once, and to control the add-on of gypsum so that the gypsum concentration of sending in the waste water of vaporizer 2 is 0.20wt.%.Embodiment 7
Experimentize based on method shown in Figure 7.The technical requirements of clarifying tank is by determining with embodiment 2 same way as.With the number of times of the phlegma flushing of reclaiming be per ten days once, and will to control the gypsum add-on so that make the gypsum concentration in the waste water that is sent to vaporizer 2 be 0.20wt.%.
Owing to all obtained above-mentioned effect in the foregoing description 1-7, therefore effect of the present invention is determined.
Claims (4)
1. method that is used to handle desulfurization wastewater, this waste water is to absorb from combustion exhaust by using alkaline reagents to make absorption agent and the FGD system of removing oxysulfide gas discharges, wherein waste water evaporates in vaporizer to reduce its volume then with the auxiliary curing agent formation solid matter of kneading, and described method comprises the following steps: in the vent line that the enrichment waste water of described vaporizer discharging is used a solid-liquid separator that is used to separate gypsum to be installed; Gypsum in described solid-liquid separator in separation and the recovery enrichment waste water; Be added to all or part of gypsum that reclaims in the described vaporizer or send in the waste water of described vaporizer and arrange the recovery gypsum of any remainder outside system or it is turned back to desulfurizer so that can reclaim by formed gypsum in desulfurizer.
2. by the described desulfurization wastewater treatment process of claim 1, wherein will pulverize and be added in the described vaporizer or be added in the waste water of sending into described vaporizer at all or part of gypsum that described solid-liquid separator reclaims.
3. method that is used to handle desulfurization wastewater, the FGD system of absorption and removal oxysulfide gas discharges this waste water from combustion exhaust by making absorption agent by the use alkaline reagents, wherein waste water evaporates in vaporizer to reduce its volume then with the auxiliary curing agent formation solid matter of kneading, described method comprises and is condensate in the steam that produced in the described vaporizer with the step that reclaims as phlegma with the step of using the phlegma that reclaimed periodically to wash described vaporizer.
4. by the treatment process of claim 1 or 2 described desulfurization wastewaters, this method also comprises the steam that produces in the described vaporizer of condensation in addition reclaiming as phlegma, and uses the phlegma that is reclaimed periodically to wash described vaporizer.
Priority Applications (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 99101283 CN1123538C (en) | 1999-01-26 | 1999-01-26 | Desulfurization waste water treating method |
| HK00105877A HK1026684A1 (en) | 1999-01-26 | 2000-09-19 | Process for the treatment of desulfurization waste water |
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 99101283 CN1123538C (en) | 1999-01-26 | 1999-01-26 | Desulfurization waste water treating method |
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| CN1262236A true CN1262236A (en) | 2000-08-09 |
| CN1123538C CN1123538C (en) | 2003-10-08 |
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| CN 99101283 Expired - Fee Related CN1123538C (en) | 1999-01-26 | 1999-01-26 | Desulfurization waste water treating method |
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| CN103896420A (en) * | 2014-04-13 | 2014-07-02 | 连芷萱 | Desulfurization waste water treatment system and method |
| US9199861B2 (en) | 2013-02-07 | 2015-12-01 | Heartland Technology Partners Llc | Wastewater processing systems for power plants and other industrial sources |
| CN106379953A (en) * | 2016-10-14 | 2017-02-08 | 北京姚魏环保技术有限公司 | Desulfurization wastewater sludge-water mixing device |
| US9617168B2 (en) | 2007-03-13 | 2017-04-11 | Heartland Technology Partners Llc | Compact wastewater concentrator using waste heat |
| CN107311373A (en) * | 2017-05-30 | 2017-11-03 | 毛强平 | The Zero-discharge treating process and device of a kind of power plant desulfurization wastewater |
| US9808738B2 (en) | 2007-03-13 | 2017-11-07 | Heartland Water Technology, Inc. | Compact wastewater concentrator using waste heat |
| CN107335323A (en) * | 2016-04-29 | 2017-11-10 | 通用电器技术有限公司 | The wet flue gas desulfurization system of zero discharging of waste liquid |
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| US9926215B2 (en) | 2007-03-13 | 2018-03-27 | Heartland Technology Partners Llc | Compact wastewater concentrator and pollutant scrubber |
| US10005678B2 (en) | 2007-03-13 | 2018-06-26 | Heartland Technology Partners Llc | Method of cleaning a compact wastewater concentrator |
| CN108946850A (en) * | 2018-08-14 | 2018-12-07 | 河北蓝江生物环保科技有限公司 | Evaporate the Retreatment method of raffinate |
| CN109110846A (en) * | 2018-08-22 | 2019-01-01 | 盛发环保科技（厦门）有限公司 | A kind of desulfurization wastewater flue gas concentration decrement and cement fixed system and technique |
-
1999
- 1999-01-26 CN CN 99101283 patent/CN1123538C/en not_active Expired - Fee Related
-
2000
- 2000-09-19 HK HK00105877A patent/HK1026684A1/en not_active IP Right Cessation
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| Publication number | Priority date | Publication date | Assignee | Title |
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| US9808738B2 (en) | 2007-03-13 | 2017-11-07 | Heartland Water Technology, Inc. | Compact wastewater concentrator using waste heat |
| US10946301B2 (en) | 2007-03-13 | 2021-03-16 | Heartland Technology Partners Llc | Compact wastewater concentrator using waste heat |
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| US9199861B2 (en) | 2013-02-07 | 2015-12-01 | Heartland Technology Partners Llc | Wastewater processing systems for power plants and other industrial sources |
| CN103896420A (en) * | 2014-04-13 | 2014-07-02 | 连芷萱 | Desulfurization waste water treatment system and method |
| CN103896420B (en) * | 2014-04-13 | 2015-09-09 | 石家庄市西姆克科技有限责任公司 | Desulfurization wastewater treatment system and method |
| CN107335323A (en) * | 2016-04-29 | 2017-11-10 | 通用电器技术有限公司 | The wet flue gas desulfurization system of zero discharging of waste liquid |
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| CN107311373A (en) * | 2017-05-30 | 2017-11-03 | 毛强平 | The Zero-discharge treating process and device of a kind of power plant desulfurization wastewater |
| CN108946850A (en) * | 2018-08-14 | 2018-12-07 | 河北蓝江生物环保科技有限公司 | Evaporate the Retreatment method of raffinate |
| CN108946850B (en) * | 2018-08-14 | 2021-07-16 | 河北蓝江生物环保科技有限公司 | Method for reprocessing evaporation raffinate |
| CN109110846A (en) * | 2018-08-22 | 2019-01-01 | 盛发环保科技（厦门）有限公司 | A kind of desulfurization wastewater flue gas concentration decrement and cement fixed system and technique |
| CN109110846B (en) * | 2018-08-22 | 2021-11-09 | 盛发环保科技（厦门）有限公司 | Desulfurization wastewater flue gas concentration reduction and cementing fixing system and process |
Also Published As
| Publication number | Publication date |
|---|---|
| CN1123538C (en) | 2003-10-08 |
| HK1026684A1 (en) | 2000-12-22 |
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