CN102765819B - Self-draining water recycling process of water circulating system - Google Patents

Self-draining water recycling process of water circulating system Download PDF

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Publication number
CN102765819B
CN102765819B CN201210249675.0A CN201210249675A CN102765819B CN 102765819 B CN102765819 B CN 102765819B CN 201210249675 A CN201210249675 A CN 201210249675A CN 102765819 B CN102765819 B CN 102765819B
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water
draining
acid
inhibiter
self
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CN102765819A (en
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吴宇锋
肖光辉
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Shaanxi Pucheng Wande Science & Technology Co., Ltd.
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WUHAN RUNERHUA TECHNOLOGY Co Ltd
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Abstract

The invention provides a self-draining water recycling process of a water circulating system. The self-draining water recycling process comprises the steps of mixing soft water corrosion inhibitor and self-draining water for complete contact and reaction; settling a mixture of the soft water corrosion inhibitor and the self-draining water to obtain soft water and sludge containing calcium and magnesium; removing the basicity of the soft water; filtering the soft water without basicity; removing salinity of the filtered soft water, and then rejecting the filtered water without salinity into the water circulating system. According to the self-draining water recycling process, due to the scientific processing process, the recycled self-draining water of the water circulating system conforms to the requirement of the quality of circulating water, and the stable and safety operation of the water circulating system can be ensured. The recycling rate of the self-draining water of the water circulating system, which is processed by the self-draining water recycling process of the water circulating system, is more than 75%, the corrosion rate of the water circulating system is reduced by 30%-50%, the sewage discharging amount is reduced by more than 80%, 20%-40% of fresh water using amount is saved, and 30%-50% of drug is saved.

Description

Circulating water system is from draining reuse technology
Technical field
The present invention relates to energy-conserving and emission-cutting technology field, particularly relate to a kind of circulating water system from draining reuse technology.
Background technology
Shortage of water resources and water pollution problems have become the significant problem of restriction human social economy Sustainable development.The industries such as petrochemical complex, iron and steel, electric power are with water and draining rich and influential family, implement the important measures that sewage recycling is these industry water-saving and emission-reducings, also be the necessary trend of water treatment field development, to industry sustainable and healthy development, ensure that Water resources security is significant.
In recirculated water operational process, in order to ensure the water quality of recirculated water, need draining, moisturizing displacement.Because the self-draining water quality of circulating water system is consistent with recirculated water, turbidity and organic content low, harmful ion content is low, and pollutant kind is few, and water quality is more clean.Just after concentration, high from draining hardness, basicity, saltiness is comparatively large, and containing a small amount of water treatment agent, therefore recoverable is worth high.Generally, be back to use in circulating water system again after caning be passed through the process of the softening desalination such as membrane technology, ion exchange resin and go.But current reuse effect is not ideal, ubiquity the problems such as technique imperfection, equipment life is short, water quality inferiority, running cost are high.
Summary of the invention
The object of the present invention is to provide a kind of circulating water system from draining reuse technology, to solve technique imperfection, equipment life that prior art exists short, the problem such as water quality inferiority, running cost are high.
To achieve these goals, circulating water system provided by the invention comprises the following steps from draining reuse technology: by soft water inhibiter with from the abundant mixing and contacting reaction of draining; Sedimentation soft water inhibiter and self-draining mixture, obtain the body refuse of hard-off degree water and calcium-magnesium-containing; The basicity of removing hard-off degree water; Cross the hard-off degree water filtering basicity; Salt in hard-off degree water after removing filtration, is then recycled into circulating water system.
From upper analysis, the present invention, by the treatment process of science, can make reuse circulating water system meet circulating water quality requirement from draining, ensures the steady safe operation of circulating water system.
Embodiment
According to embodiment, the present invention is described in further details below.
The invention provides a kind of circulating water system from draining reuse technology, during enforcement, need to relate to multinomial equipment, comprise line mixer, reactor, settling tank, multi-functional fine filter, electrodialytic desalting equipment and regulate and distribute device.Basic step is: circulating water system enters line mixer from draining through pump or system pressure, adds soft water inhibiter and mixes; Then the mixture of the two enters reactor, enters settling tank by reactor outlet; Enter clean water basin by settling tank overflow, filter through fine filter and enter electrodialytic desalting equipment, after desalination, be back to use circulating water system.Wherein, regulate and distribute device can according to the conductivity adjustment of system from drainage sunk well amount, reuse circulating water system from the ratio of desalinization of drain treatment apparatus.
Wherein, circulating water system is from draining after circulating water system is discharged, and the dosage adding soft water inhibiter is that 50 ~ 500 mg/ rise from draining, and preferable amount is that 150 ~ 300 mg/ rise from draining, soft water inhibiter and sewer hybrid reaction time are 10 ~ 60min, and the preferred reaction time is 20 ~ 40min.Preferably, soft water inhibiter comprises sequestrant, precipitation agent, inhibiter and pH adjusting agent.Sequestrant is one of them or wherein multiple mixture of nitrilotriacetic acid sodium, aminodiacetic acid sodium, disodium ethylene diamine tetraacetate.Precipitation agent is one of them or wherein multiple mixture of polyacrylamide, Walocel MT 20.000PV, Sodium glycocollate.Inhibiter is one of them or wherein multiple mixture of 2-tetrahydroglyoxaline, bi-imidazoline quaternary ammonium salt, 4-methylimidazole quinoline, 17 alkenyl amine ethyl imidazol(e) hyamines.PH adjusting agent is one of them or wherein multiple mixture of sodium carbonate, sodium hydroxide, calcium hydroxide.During proportioning soft water inhibiter, according to the difference of the component such as hardness ions, basicity ion distribution in sewer, the proportioning of sequestrant, precipitation agent, inhibiter is corresponding with consumption also different, when hydrocarbonate content is lower, when hardness content is higher, the consumption of suitable increase sequestrant, precipitation agent, can obtain good bating effect.Owing to the addition of tetrahydroglyoxaline series inhibiter component in sequestrant, greatly reduce the corrodibility of sequestrant to relevant device in use, transport, storage.
Circulating water system after mixing enters reactor from draining through motorized valve, under meter, and the reaction times is preferably 10 ~ 60min, and further preferably, the reaction times controls at 20 ~ 40min.
Reacted circulating water system enters settling tank from draining, and the settling time is preferably 10 ~ 150min, and the preferred settling time is 60 ~ 120min further.
Settling tank water outlet is through acid adding, and such as sulfuric acid, after regulating basicity, enters multi-functional filter through tank.Water in clean water basin enters fine filter through high-pressure pump, the insolubles in filtered water.
The water outlet of fine filter enters electrodialytic desalting equipment, carries out desalting treatment.
Adopt the ratio regulating and distributing the device adjustment self-draining treatment capacity of circulating water system and recirculated water internal circulating load to be 1:100 ~ 1:1100, preferred ratio is 1:200 ~ 1:800, and the ratio of desalinization controlling above-mentioned treatment unit is 30% ~ 90%, and preferred ratio of desalinization is 50% ~ 90%.
Further, adopt the circulating water system corrosion caused from draining reuse from draining reuse anti-incrustation corrosion inhibitor controlled circulation water system, be that 10min ~ 100 mg/ rises recirculated water from draining reuse anti-incrustation corrosion inhibitor consumption, preferable amount is that 60mg ~ 90 mg/ rises recirculated water.Preferably, of the present inventionly to comprise containing phosphine heteropolyacid zinc salt inorganic polymer inhibiter, multi-hydroxy carboxy acid's salt organic inhibitor, Azole Corrosion Inhibitors and dirt dispersion agent from draining reuse anti-incrustation corrosion inhibitor.Containing one of them or wherein multiple mixture that phosphine zinc heteropolyacid salt inorganic polymer inhibiter is phosphato-molybdic heteropolyacid, phosphorus heteropoly tungstic acid, organic phosphine molybdenum heteroacid, organophosphono-heteropolytungstic acid, phosphorus molybdenum heteroacid zinc, phosphorus heteropoly tungstic acid zinc, organic phosphine molybdenum heteroacid zinc, organic tungsten heteropolyacid zinc.Multi-hydroxy carboxy acid's salt organic inhibitor is one of them or wherein multiple mixture of tartrate, citric acid, Whitfield's ointment, phenylformic acid, oxysuccinic acid, glyconic acid, folic acid, tannin, sodium tartrate, Trisodium Citrate, sodium salicylate, Sodium Benzoate, sodium malate, gluconic acid sodium salt, folic acid sodium salt, tannin sodium salt.Azole Corrosion Inhibitors is one of them or wherein multiple mixture of benzotriazole, methyl benzotriazazole, thyroidan, carboxy benzotriazole.Dirt dispersion agent is one of them or wherein multiple mixture of polyacrylic acid, polymaleic acid, poly-aspartic-acid, poly-epoxy succinic acid, maleic acid-acrylic acid copolymer, vinylformic acid-2-acrylamide-2-methyl propane sulfonic multipolymer, acrylic acid-acrylic ester-sulfonate, acrylic acid-acrylic acid hydroxypropyl acrylate.
The corrosive ion such as fouling tendency ion and sodium, potassium, chlorine, sulfate radical such as hardness ions, basicity ion of circulating water system containing high density in draining.These ions result in fouling and the etching problem of circulating water system.In softening-demineralising process, circulating water system adds soft water inhibiter in draining, sequestrant (its metalloid core ion has empty 3d track) wherein and hardness ions generation chelatropic reaction, pH value regulator regulates water pH value to promote that chelatropic reaction carries out in alkalescence.In settling process, the inner complex particle accumulation that the precipitation agent in soft water inhibiter is tiny by dispersion becomes larger granule thus accelerates the settling velocity of inner complex particle.That removes the hardness ions such as most of calcium, magnesium in water.In settling process, due to the continuity distribution character of settling particle particle diameter, more tiny particle precipitation is comparatively slow, and stable suspersion, in softening water, is removed by multi-functional filter, and residual basicity ion is removed by sulfuric acid reaction.Softening water after process filters further through fine filter, and enter electrodialysis appts and carry out desalination, the de-salted water after desalination is back to use circulating system.
Therebetween, the circulating water system corrosion caused from draining reuse anti-incrustation corrosion inhibitor control of sewage disposal Water circulation is adopted; Adopt and regulate and distribute the ratio that device regulates the self-draining quantity discharged of recirculated water and recirculated water internal circulating load, control ratio of desalinization.Organic compound major part is by softening-desalting system, be removed on a small quantity, and exist in polymer form containing phosphine heteropolyacid zinc salt inorganic polymer inhibiter, softening-salt-removal steps is to phosphorus, tungsten, zinc three kinds of components to remove ratio completely the same, be conducive to reusing and stability contorting of recirculated water Chinese medicine, containing phosphine heteropolyacid zinc salt inorganic polymer inhibiter, multi-hydroxy carboxy acid's salt organic inhibitor, the Synergistic inhibition of Azole Corrosion Inhibitors, Combination protective membrane can be formed in metallic surface, there is excellent corrosion mitigating effect, effectively can prevent aqueous corrosion, inhibiting point corrosion and strong brine corrosion.The conductance of producing water and recirculated water is detected by the conductivity meter regulating and distributing device, according to circulation electrical conductivity of water, produce water conductivity, water circulation control circulating water system from the size of drainage sunk well amount, circulating water system from the ratio of desalinization of draining recycling and processing equipment, make circulating water system basic consistent with moisturizing from draining specific conductivity, meet the operation standard of recirculated water.
When applying the present invention to a concrete situation, can following steps be adopted:
1, by system sewerage (its character is as table 1) and soft water inhibiter sodium carbonate, the sodium hydroxide of 60%, the Walocel MT 20.000PV of 5% of 10% (the nitrilotriacetic acid sodium of 10%, the 2-tetrahydroglyoxaline of 15%) pre-mixing, soft water inhibiter add-on is that 150mg/ rises from draining.
2, after line mixer fully stirs, react after 30 minutes in retort, gravity natural subsidence 1 hour in settling tank, can certainly by other industrial sedimentation utility appliance, and inner complex body refuse falls to bottom settling tank.In other embodiments, soft water inhibiter mixes with sewer and also can mix in stirred pot, line mixer or other commercial mixing apparatus.
3, settling tank top clear liquor filters through multi-functional filter, adds sulfuric acid removing basicity, entering electrodialytic desalting equipment, being then back to use circulating water system through regulating and distributing device.When filtering, batch filtration can be adopted, continous way is filtered, other mode such as aided filter means and combination thereof.The mediation of softening-de-salted water and recirculated water can be carried out in stirred pot, line mixer or other commercial mixing apparatus.
4, adopt and regulate and distribute device and regulate the quantity discharged of Wastewater Form Circulating Cooling Water and the ratio of recirculated water internal circulating load to be 1:500, regulate the ratio of desalinization of above-mentioned treatment unit to be 87%.
5, add in recirculated water from draining reuse anti-incrustation corrosion inhibitor (phospho-wolframic acid zinc: 15%; Tartrate: 20%; Methyl benzotriazazole: 3%; Polyacrylic acid: 40%; Water: 22%), anti-incrustation corrosion inhibitor can adopt impact type, continous way adds or adopt other power-equipment and mixing dosing method to add circulating water system.
Table 1: water quality before and after softening-desalination
Index name Sewer Softening desalination water
Hardness 860 40
Basicity 592 0
Calcium 625 25
Conductance 2200 335
Chlorine root 90 14
Sulfate radical 100 29
When applying the present invention to another concrete situation, can following steps be adopted:
1, by system sewerage (its character is as table 2) and soft water inhibiter sodium carbonate, the sodium hydroxide of 30%, the polyacrylamide of 4% of 30% (disodium ethylene diamine tetraacetate of 20%, the bi-imidazoline quaternary ammonium salt of 16%) pre-mixing, soft water inhibiter add-on is 200mg/ liter.
2, after line mixer fully stirs, react after 40 minutes in retort, gravity natural subsidence 1.5 hours in settling tank, inner complex body refuse falls to bottom settling tank.
3, settling tank top clear liquor is after multi-functional device of worrying too much filters, and after adding sulfuric acid removing basicity, entering electrodialytic desalting, being then back to use circulating water system through regulating and distributing device.
4, adopt the ratio regulating and distributing the device adjustment self-draining treatment capacity of circulating water system and recirculated water internal circulating load to be 1:650, regulate the ratio of desalinization of above-mentioned treatment unit to be 80%.
5, add in recirculated water from draining reuse anti-incrustation corrosion inhibitor (phospho-molybdic acid zinc: 20%; Gluconic acid: 20%; Benzotriazole: 2%; Poly-epoxy succinic acid: 35%; Water: 23%),
Table 2: water quality before and after softening-desalination
Index name Sewer Softening desalination water
Hardness 647 38
Basicity 425 0
Calcium 429 20
Conductance 1850 462
Chlorine root 134 35
Sulfate radical 113 34
In sum, when applying the reusing sewage after process of the present invention to circulating water system, the fresh water of 20% ~ 40% can be replaced, reduce by the blowdown of more than 80%, reduce circulating water system erosion rate 30% ~ 50%, save anti-incrustation corrosion inhibitor medicament 30% ~ 50%.Visible, present invention process is simple, reduced investment, process cost are low.Application the present invention, only need, by a small amount of equipment, just can utilize simple method that Substitute For Partial fresh water after reuse after Circulating water effluent Water warfare is back to use circulating water system.The magnitude of recruitment of fresh water can be reduced, reduce quantity of wastewater effluent, save the working cost of circulating water system, realize economic benefit, social benefit optimization.
As known by the technical knowledge, the present invention can be realized by other the embodiment not departing from its spirit or essential feature.Therefore, above-mentioned disclosed embodiment, with regard to each side, all just illustrates, is not only.Within the scope of the present invention all or be all included in the invention being equal to the change in scope of the present invention.

Claims (5)

1. circulating water system is from a draining reuse technology, it is characterized in that comprising the steps:
Soft water inhibiter with from draining through line mixer, the abundant mixing and contacting reaction of retort;
The sedimentation in settling bowl of said mixture material, obtain hard-off degree water on settling bowl upper strata, lower floor isolates the body refuse of calcium-magnesium-containing;
Fully contact, to remove basicity with above-mentioned hard-off degree water with sulfuric acid;
Adopt filter plant except the middle suspended substance that anhydrates;
Adopt salt in electrodialysis appts process water, be then recycled into circulating water system;
Adopt and regulate and distribute the ratio that device regulates the self-draining quantity discharged of circulating water system and recirculated water internal circulating load, control the ratio of desalinization of electrodialysis appts;
Adopt the circulating water system corrosion that special anti-incrustation corrosion inhibitor controls to cause from draining reuse, described soft water inhibiter consumption is that 50mg ~ 500mg/ rises from draining, described soft water inhibiter be 10min ~ 60min from the draining hybrid reaction time, the settling time is 10min ~ 150min; Described special anti-incrustation corrosion inhibitor consumption is that 10mg ~ 100mg/ rises recirculated water; The described device that regulates and distributes regulates the ratio of the self-draining quantity discharged of circulating water system and recirculated water internal circulating load to be 1:100 ~ 1:1100, and the ratio of desalinization regulating electrodialysis appts is 30% ~ 90%;
Described soft water inhibiter is made up of sequestrant, precipitation agent, inhibiter and pH adjusting agent, described sequestrant is nitrilotriacetic acid sodium, aminodiacetic acid sodium, disodium ethylene diamine tetraacetate or its mixture, described precipitation agent is polyacrylamide, Walocel MT 20.000PV, Sodium glycocollate or its mixture, described inhibiter is 2-tetrahydroglyoxaline, bi-imidazoline quaternary ammonium salt, 4-methylimidazole quinoline, 17 alkenyl amine ethyl imidazol(e) hyamines or its mixture, and described pH adjusting agent is sodium carbonate, sodium hydroxide, calcium hydroxide or its mixture;
Described special anti-incrustation corrosion inhibitor is by containing phosphine heteropolyacid zinc salt inorganic polymer inhibiter, multi-hydroxy carboxy acid's salt organic inhibitor, Azole Corrosion Inhibitors and dirt dispersion agent composition, described is phosphorus molybdenum heteroacid zinc containing phosphine heteropolyacid zinc salt inorganic polymer inhibiter, phosphorus heteropoly tungstic acid zinc, organic phosphine molybdenum heteroacid zinc or its mixture, described multi-hydroxy carboxy acid's salt organic inhibitor is sodium tartrate, Trisodium Citrate, sodium salicylate, Sodium Benzoate, sodium malate, gluconic acid sodium salt, folic acid sodium salt, tannin sodium salt or its mixture, described Azole Corrosion Inhibitors is benzotriazole, methyl benzotriazazole, thyroidan, carboxy benzotriazole or its mixture, described dirt dispersion agent is polyacrylic acid, polymaleic acid, poly-aspartic-acid, poly-epoxy succinic acid, maleic acid-acrylic acid copolymer, vinylformic acid-2-acrylamide-2-methyl propane sulfonic multipolymer, acrylic acid-acrylic ester-sulfonate, acrylic acid-acrylic acid hydroxypropyl acrylate or its mixture.
2. circulating water system according to claim 1 is from draining reuse technology, it is characterized in that:
Described soft water inhibiter be 20min ~ 40min from the draining hybrid reaction time; Settling time is 60min ~ 120min.
3. circulating water system according to claim 1 is from draining reuse technology, it is characterized in that:
Described soft water inhibiter consumption is that 150mg ~ 300mg/ rises from draining.
4. circulating water system according to claim 1 is from draining reuse technology, it is characterized in that:
Described special anti-incrustation corrosion inhibitor consumption is that 60mg ~ 90mg/ rises recirculated water.
5. circulating water system according to claim 1 is from draining reuse technology, it is characterized in that:
The described device that regulates and distributes regulates the ratio of the self-draining quantity discharged of circulating water system and recirculated water internal circulating load to be 1:200 ~ 1:800; The ratio of desalinization regulating electrodialysis appts is 50% ~ 90%.
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