CN104230063A - Method for treating high-concentration salt-containing waste water on irbesartan aminated section and system thereof - Google Patents
Method for treating high-concentration salt-containing waste water on irbesartan aminated section and system thereof Download PDFInfo
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- CN104230063A CN104230063A CN201410522516.2A CN201410522516A CN104230063A CN 104230063 A CN104230063 A CN 104230063A CN 201410522516 A CN201410522516 A CN 201410522516A CN 104230063 A CN104230063 A CN 104230063A
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Abstract
The invention relates to the technical field of pharmaceutical waste water treatment and specifically relates to a method for treating high-concentration salt-containing waste water on an irbesartan aminated section and a system thereof, and the method comprises the following steps of: oxidizing and filtering the high-concentration salt-containing waste water on the irbesartan aminated section to remove organic substances and suspension colloids from the waste water; performing desalting to the pretreated high-concentration salt-containing waste water on the irbesartan aminated section through a bipolar membrane device, and directly conversing sodium chloride from the waste water into hydrochloric acid and sodium hydroxide solution with relative concentration. In the method and the system, there are no secondary pollution and solid waste production, the removed salt can be directly conversed into hydrochloric acid and sodium hydroxide solution with a certain concentration and reused to the primary production process, thus the method and the system have the advantages of excellent desalting effect, resources and energy saving, simple processes and low operating cost.
Description
Technical field
The present invention relates to pharmaceutical wastewater processing technology field, be specifically related to a kind of irbesartan amination workshop section high-concentration salt-containing wastewater treatment process and system thereof.
Background technology
Irbesartan is treatment essential hypertension, has important Renoprotective Effect, can slow down the progress of diabetic nephropathy.For diabetes B nephrotic, if suffer from hypertension simultaneously, irbesartan can slow down the progress of ephrosis.
Essential hypertension a kind ofly continues to raise as the Progressive symmetric erythrokeratodermia cardiovascular disease of feature with arteriotony, is the modal chronic disease of global human, is heart trouble, cerebro-vascular diseases, nephropathy occur and the main Hazard Factor of death.China is populous, and along with the astogeny of population, essential hypertension sickness rate is in ascendant trend year by year in recent years.Irbesartan class antihypertensive drug is as the effective medicine of one, and turnout at home rises year by year.
The synthesis of irbesartan medicine comprises: amination workshop section, hydrolysis workshop section, acidylate cyclization workshop section, condensation workshop section and refinement.In the extraction stratification operation of amination workshop section, oil-phase product enters follow-up workshop section, a large amount of layering water is discharged with waste water formation, quantity discharged is about 5.31 tons of (waste water)/tons (product), layering waste water component comprises: water 74 ~ 76% (W/W), sodium-chlor 12 ~ 15% (W/W), methyl alcohol 10 ~ 12% (W/W), cyanamide 0.3 ~ 0.6% (W/W), methylene dichloride trace layering waste water accounts for more than 8% of whole displacement product, there is organic concentration high, the feature that salt content is high.As directly entered biochemical treatment system, system will be caused normally to run.Current processing mode enters two kinds of processing modes of biochemical treatment system after mainly containing distillation desalination and dilution.
Distillation desalination adopts the mode of triple effect underpressure distillation or MVR distillation, the moisture in waste water and some volatile organism is distilled with water vapor form, and residue dope goes out the waste residue containing sodium-chlor crystallization through crystallization kettle Crystallization Separation.This type of waste residue, due to containing the difficult volatile organic compounds of part and building-up reactions intermediate, cannot directly be utilized, and only have as industrial dangerous waste process, very easily cause secondary pollution, and running cost is high.The method entering biochemical treatment system after dilution, because of salt excessive concentration, for meeting the requirement of biochemical treatment water inlet, need be diluted more than at least 20 times and just can meet the demands, causing a large amount of wastes of water, have larger problem in actually operating.Therefore, treatment process and the system thereof of developing a kind of irbesartan amination workshop section high-concentration salt-containing wastewater also just become one of study hotspot.
Summary of the invention
The object of this invention is to provide a kind of irbesartan amination workshop section high-concentration salt-containing wastewater treatment process and system thereof, non-secondary pollution, produce without solid waste, the salt that removes can be converted into certain density hydrochloric acid and sodium hydroxide solution, reuse to front end production process, have desalting effect good, economize on resources and the energy, the advantage such as technique is simple, working cost is low.
For solving the problems of the technologies described above, the technical solution used in the present invention is:
A kind of irbesartan amination workshop section high-concentration salt-containing wastewater treatment process, comprises the steps:
(1) pre-treatment: by irbesartan amination workshop section high-concentration salt-containing wastewater through peroxidation and filtration treatment, to remove organic substance in waste water and suspensoid;
(2) pretreated irbesartan amination workshop section high-concentration salt-containing wastewater is carried out desalting treatment by bipolar membrane device, the sodium-chlor in waste water is converted into hydrochloric acid and the sodium hydroxide solution of respective concentration, to reach the object of desalination.
Further, the waste water that described irbesartan amination workshop section high-concentration salt-containing wastewater discharges when being amination in irbesartan production process, its component comprises: water 74 ~ 76% (W/W), sodium-chlor 12 ~ 15% (W/W), methyl alcohol 10 ~ 12% (W/W), cyanamide 0.3 ~ 0.6% (W/W), methylene dichloride trace.
Further, described oxide treatment adopts Fenton oxidation processing mode, and in treating processes, control ph is between 3 ~ 4, to remove low molecular weight organic matters (being mainly solvent based) in waste water and hydrocyanic ion, prevents it from destroying membrane material.
Further, described filtration treatment is carried out in filtration unit, it is that the filter element filtering device of 0.45 ~ 1.0 μm or filter cloth order number are greater than 8000 object flame filter presses that described filtration unit comprises precision, to remove suspensoid in waste water and macromolecular colloid organic substance.
Further, the filtered version of described filtration treatment determines by processing the water yield, and day output is less than 10m
3, adopt filter element filtering device to filter; Day output is greater than 20m
3, adopt flame filter press to filter; Day output is at 10 ~ 20m
3time, filter element filtering device can be adopted or filter flame filter press and filter
Further, described bipolar membrane device comprises cathode compartment, sour room, salt room, alkali room, anolyte compartment, between each room by anions and canons exchange membrane and or pole film partitioned arrangement composition, its arrangement mode is cationic exchange membrane-Bipolar Membrane-anion-exchange membrane.
Further, the plate current density of described bipolar membrane device is 280-320A/m
2, the spacing 4 ~ 8mm between each room, arranges flow-guiding channel in the middle of dividing plate; In acid room and alkali room, solution crosses Flow Velocity 4 ~ 8cm/s, salt room solution crosses Flow Velocity 8 ~ 12cm/s.
Further, acid in described desalting treatment process, alkali, salt three kinds of solution arrange independently basin and recycle pump respectively, by controlling the side line outflow rate of corresponding circulating pump, control waste water ratio of desalinization and concentration that is sour, alkaline solution; Controlling ratio of desalinization in described desalting treatment process is 80 ~ 85%, and concentration of hydrochloric acid is 10 ~ 12% (W/W), and naoh concentration is 12 ~ 15% (W/W).
Further, the treatment system that described nigrosine produces high-concentration salt-containing wastewater comprises: waste water tank, broken cyanide device, filtration unit, bipolar membrane device, recirculated cooling water heat-exchanger rig, acid case, alkali case, described waste water tank, broken cyanide device, filtration unit, be interconnected by lift pump or topping-up pump and connecting tube between bipolar membrane device, be interconnected by pump and connecting tube between described bipolar membrane device and recirculated cooling water heat-exchanger rig, salt water tank and salt water circulating pump is provided with between described filtration unit and bipolar membrane device, described sour case is communicated with the sour room in described bipolar membrane device by acid circulating pump, described alkali case is communicated with the alkali room in described bipolar membrane device by alkali recycle pump.
Further, described salt water circulating pump exit end is provided with ready-package candle filter, to filter the suspensoid produced in demineralising process.
Ion-exchange in bipolar membrane device of the present invention is intermembranous is elastic baffle with runner, and anode adopts Ti-Ru electrode, and negative electrode adopts stainless steel electrode, the following (see figure 2) of specific works principle:
Waste water after filtration is pumped into the salt room of bipolar membrane device, and pump into deionized water at acid, alkali in room, room, pole adds the alkali lye of 10.0 ~ 15.0% (W/W) concentration simultaneously; The cathode and anode of bipolar membrane device be connected with the negative, positive pole of direct supply respectively, controlling DC electric field current density is 280 ~ 320A/m
2, voltage across poles 40V; Acid, alkali, salt room solution adopt recycle pump to circulate in respective chambers respectively, control at 1 ~ 40 DEG C by heat-exchanger rig by each room solution temperature, set temperature sensor in Controlling System, when exceeding design temperature, strengthen interchanger coolant rate, damage membrane module to prevent excessive temperature.
Chlorion in waste water is under electric field action, and selectivity arrives sour room through anion-exchange membrane, is combined generates hydrochloric acid with the hydrogen ion that Bipolar Membrane produces; Sodium ion selective in waste water arrives alkali room through cationic exchange membrane, is combined generates sodium hydroxide with the hydroxide ion that Bipolar Membrane produces, thus realizes the sodium-chlor in waste water to be separately converted to corresponding acid and alkali, achieves the object of desalination.
Solution in sour room in bipolar membrane device, alkali room, salt room all adopts recycle pump alone cycle, and pump discharge side line goes out to flow finished product, controls ratio of desalinization, acid concentration, alkali concn respectively by the side line outflow rate controlling different recycle pump.Under the prerequisite of comprehensive accounting running cost, control ratio of desalinization 80 ~ 85%, concentration of hydrochloric acid controls at 10 ~ 12% (W/W), and naoh concentration controls at 12 ~ 15% (W/W).
Positively effect of the present invention is: rely on oxidation and the combination of filtering pre-treatment and bipolar membrane device, change the conventional process mode of irbesartan amination workshop section high-concentration salt-containing wastewater.Sodium-chlor in waste water is regenerated hydrochloric acid and sodium hydroxide, completely avoid the secondary pollution problem of the waste residue that original distil process produces; The hydrochloric acid produced and sodium hydroxide inclusion-free, purity is high, can direct reuse to the production process of front end, use the present invention, can by whole production process more than 60 ~ 80% acid, alkali recycle, greatly reduce the consumption of acid, alkali in production process; Meanwhile, the impact of salt on follow-up Sewage treatment systems is also reduced.Brine waste after process of the present invention, sodium chloride content can be reduced to 15 ~ 20g/L, substantially meets the basic saltiness requirement of biochemical wastewater treatment system.Contrast with Conventional espresso process, treatment method produces without any secondary pollution, the acid generated, alkali can direct reuse to production process, and energy consumption cost is less than 180 yuan/m
3waste water.The present invention also can substitute current dilution process mode, reduces waste water total release at double.
accompanying drawing illustrates:
Fig. 1 is the process flow diagram of E Shabeitan amination workshop section of the present invention high-concentration salt-containing wastewater treatment system;
Fig. 2 is bipolar membrane device principle of work schematic diagram of the present invention.
embodiment:
The following stated is only preferred embodiment of the present invention, does not therefore limit protection scope of the present invention.
Embodiment one, see shown in Fig. 1 to Fig. 2:
Irbesartan amination workshop section brine waste: day quantity discharged be about 30 tons, brine waste component comprises: water 74.68% (W/W), sodium-chlor 13.05% (W/W), methyl alcohol 11.50% (W/W), cyanamide 0.35% (W/W), methylene dichloride trace.
Irbesartan amination workshop section high-concentration salt-containing wastewater treatment system comprises: 60m
3volume waste water tank 1, lift pump 1, topping-up pump 1, integral type oxidation broken cyanide treatment unit 1 overlaps, flame filter press 1,10m
3volume salt water tank 1,10m
31, volumetric acid case, 10m
31, volume alkali case, acid circulating pump 1, alkali recycle pump 1, salt water circulating pump 1, bipolar membrane device 1 overlap, recirculated cooling water heat-exchanger rig 1 overlaps.
A kind of irbesartan amination workshop section's high-concentration salt-containing wastewater treatment process and system thereof, comprise the steps and technological process:
(1) preprocessing process:
1) the irbesartan amination workshop section high-concentration salt-containing wastewater collected separately is promoted to integral type oxidation broken cyanide treatment unit by lift pump sequence batch (waste water tank, with hydrochloric acid, waste water ph is adjusted to 3 ~ 4, quantitatively add oxidizing agent sodium hypochlorite and alkali, make the low molecular weight organic matters in waste water and hydrocyanic ion oxygenolysis;
2) by the secondary waste water adjusted to ph to 9 after oxide treatment, being promoted to filter cloth order number by topping-up pump is 10000 object flame filter presses, and clear liquid gravity flow enters salt water tank, residue collection outward transport process;
(2) desalting treatment process:
1) sour case and alkali case are put into deionized water respectively, room, pole adds the alkali lye that concentration is 10.0% (W/W);
2) open bipolar membrane device, current density between cathode and anode is controlled at 320A/m
2, voltage across poles 40V, start acid, alkali, salt recycle pump, control sour room, alkali room solution crosses Flow Velocity 8cm/s, salt room solution crosses Flow Velocity 12cm/s, the spacing 8mm between each room, and arrange flow-guiding channel in the middle of dividing plate, each room solution temperature controls at 30 ~ 40 DEG C;
3) after in acid, alkali, salt water tank, respective concentration reaches set(ting)value, the side line opening corresponding circulating pump respectively goes out stream, under the prerequisite meeting ratio of desalinization 85%, acid concentration 12%, alkali concn 15%, salt solution: acid: the side line of alkali goes out stream than controlling at 1:1.22:1.14.
Anion-exchange membrane in described bipolar membrane device is Selemion CMV high-durability film, cationic exchange membrane is the high temperature resistant alkali resistance film of Selemion AHO, Bipolar Membrane is Neosebta BP-1 film, the intermembranous elastic baffle being provided with band runner of ion-exchange, anode adopts Ti-Ru electrode, and negative electrode adopts 304 stainless steel electrodes.Described salt water circulating pump exit end is provided with ready-package candle filter, to filter the suspensoid produced in demineralising process.
Under the prerequisite by above step operation, system runs 10 hours every day.After end of run, adopt 5.0% sodium hydroxide solution, inject acid, the indoor soaking and washing of salt 30 minutes, waste liquid enters salt water tank.
Find within cycle of operation of 60 days altogether, be under the condition of 13% (W/W) at former water sodium chloride concentration, by adjustment recycle pump side line water flow, all the time can ensure that water outlet sodium chloride concentration is less than 1.0% (W/W), comprehensive power consumption is about 225kwh/ ton (waste water).Recovery is produced concentration of hydrochloric acid and is about 12%, and alkali concn is about 15%, and the rear de-salted water of process directly enters plant area's Sewage treatment systems and carries out subsequent disposal.In whole treatment cycle, membrane module is without considerable change.
Embodiment two, see shown in Fig. 1 to Fig. 2:
Irbesartan amination workshop section brine waste: day quantity discharged be about 15 tons, brine waste component mainly comprises: water 75.17% (W/W), sodium-chlor 14.01% (W/W), methyl alcohol 10.23% (W/W), cyanamide 0.5% (W/W), methylene dichloride trace.
Irbesartan amination workshop section high-concentration salt-containing wastewater treatment system comprises: 60m
3volume waste water tank 1, lift pump 1, topping-up pump 1, integral type oxidation broken cyanide treatment unit 1 overlaps, flame filter press 1,10m
3volume salt water tank 1,10m
31, volumetric acid case, 10m
31, volume alkali case, acid circulating pump 1, alkali recycle pump 1, salt water circulating pump 1, bipolar membrane device 1 overlap, recirculated cooling water heat-exchanger rig 1 overlaps.
A kind of irbesartan amination workshop section's high-concentration salt-containing wastewater treatment process and system thereof, comprise the steps and technological process:
(1) preprocessing process:
1) the irbesartan amination workshop section high-concentration salt-containing wastewater collected separately is promoted to integral type oxidation broken cyanide treatment unit by lift pump sequence batch (waste water tank, with hydrochloric acid, waste water ph is adjusted to 3 ~ 4, quantitatively add oxidizing agent sodium hypochlorite and alkali, make the low molecular weight organic matters in waste water and hydrocyanic ion oxygenolysis;
2) by the secondary waste water adjusted to ph to 9 after oxide treatment, being promoted to filter cloth order number by topping-up pump is 10000 object flame filter presses, and clear liquid gravity flow enters salt water tank, residue collection outward transport process;
(2) desalting treatment process:
1) sour case and alkali case are put into deionized water respectively, room, pole adds the alkali lye that concentration is 15.0% (W/W);
2) open bipolar membrane device, current density between cathode and anode is controlled at 280A/m
2, voltage across poles 40V, start acid, alkali, salt recycle pump, control sour room, alkali room solution crosses Flow Velocity 4cm/s, salt room solution crosses Flow Velocity 8cm/s, the spacing 4mm between each room, and arrange flow-guiding channel in the middle of dividing plate, each room solution temperature controls at 20 ~ 30 DEG C;
3) after in acid, alkali, salt water tank, respective concentration reaches set(ting)value, the side line opening corresponding circulating pump respectively goes out stream, under the prerequisite meeting ratio of desalinization 80%, acid concentration 10%, alkali concn 12%, salt solution: acid: the side line of alkali goes out stream than controlling at 1:1.20:1.10.
Anion-exchange membrane in described bipolar membrane device is Selemion CSO type monovalent ion permselective membrane, cationic exchange membrane is Selemion ASV type monovalent ion permselective membrane, Bipolar Membrane is Neosebta BP-1 film, the intermembranous elastic baffle being provided with band runner of ion-exchange, anode adopts Ti-Ru electrode, and negative electrode adopts 304 stainless steel electrodes.Described salt water circulating pump exit end is provided with ready-package candle filter, to filter the suspensoid produced in demineralising process.
Under the prerequisite by above step operation, system runs 10 hours every day.After end of run, adopt 5.0% sodium hydroxide solution, inject acid, the indoor soaking and washing of salt 30 minutes, waste liquid enters salt water tank.
Find within cycle of operation of 60 days altogether, be under the condition of 14.01% (W/W) at former water sodium chloride concentration, by adjustment recycle pump side line water flow, all the time can ensure that water outlet sodium chloride concentration is less than 2.0% (W/W), comprehensive power consumption is about 240kwh/ ton (waste water).Recovery is produced concentration of hydrochloric acid and is about 10%, and alkali concn is about 12%, and the rear de-salted water of process directly enters plant area's Sewage treatment systems and carries out subsequent disposal.In whole treatment cycle, membrane module is without considerable change.
The above is only better embodiment of the present invention, therefore all equivalences done according to the ultimate principle described in patent claim of the present invention change or modify, and are included in patent claim of the present invention.
Claims (10)
1. an irbesartan amination workshop section high-concentration salt-containing wastewater treatment process, is characterized in that comprising the steps:
(1) pre-treatment: by irbesartan amination workshop section high-concentration salt-containing wastewater through peroxidation and filtration treatment, to remove organic substance in waste water and suspensoid;
(2) pretreated irbesartan amination workshop section high-concentration salt-containing wastewater is carried out desalting treatment by bipolar membrane device, the sodium-chlor in waste water is converted into hydrochloric acid and the sodium hydroxide solution of respective concentration.
2. irbesartan amination workshop section according to claim 1 high-concentration salt-containing wastewater treatment process, it is characterized in that: the waste water discharged when described irbesartan amination workshop section high-concentration salt-containing wastewater is amination in irbesartan production process, its component comprises: water 74 ~ 76% (W/W), sodium-chlor 12 ~ 15% (W/W), methyl alcohol 10 ~ 12% (W/W), cyanamide 0.3 ~ 0.6% (W/W), methylene dichloride trace.
3. irbesartan amination workshop section according to claim 1 high-concentration salt-containing wastewater treatment process, is characterized in that: oxide treatment adopts Fenton oxidation processing mode, and in treating processes, control ph is between 3 ~ 4.
4. irbesartan amination workshop section according to claim 1 high-concentration salt-containing wastewater treatment process, it is characterized in that: described filtration treatment is carried out in filtration unit, it is that the filter element filtering device of 0.45 ~ 1.0 μm or filter cloth order number are greater than 8000 object flame filter presses that described filtration unit comprises precision.
5. irbesartan amination workshop section according to claim 4 high-concentration salt-containing wastewater treatment process, is characterized in that: the filtered version of described filtration treatment determines by processing the water yield, and day output is less than 10m
3, adopt filter element filtering device to filter; Day output is greater than 20m
3, adopt flame filter press to filter; Day output is at 10 ~ 20m
3time, filter element filtering device can be adopted or filter flame filter press and filter.
6. irbesartan amination workshop section according to claim 1 high-concentration salt-containing wastewater treatment process, it is characterized in that: described bipolar membrane device comprises cathode compartment, sour room, salt room, alkali room, anolyte compartment, between each room by anions and canons exchange membrane and or pole film partitioned arrangement composition, its arrangement mode is cationic exchange membrane-Bipolar Membrane-anion-exchange membrane.
7. irbesartan amination workshop section according to claim 1 high-concentration salt-containing wastewater treatment process, is characterized in that: the plate current density of described bipolar membrane device is 280-320A/m
2, the spacing 4 ~ 8mm between each room, arranges flow-guiding channel in the middle of dividing plate; In acid room and alkali room, solution crosses Flow Velocity 4 ~ 8cm/s, salt room solution crosses Flow Velocity 8 ~ 12cm/s.
8. irbesartan amination workshop section according to claim 1 high-concentration salt-containing wastewater treatment process, it is characterized in that: acid in described desalting treatment process, alkali, salt three kinds of solution arrange independently basin and recycle pump respectively, by controlling the side line outflow rate of corresponding circulating pump, control waste water ratio of desalinization and concentration that is sour, alkaline solution; Controlling ratio of desalinization in described desalting treatment process is 80 ~ 85%, and concentration of hydrochloric acid is 10 ~ 12% (W/W), and naoh concentration is 12 ~ 15% (W/W).
9. the treatment system of the irbesartan amination workshop section high-concentration salt-containing wastewater treatment process according to claim 1 or 6, it is characterized in that comprising: waste water tank, broken cyanide device, filtration unit, bipolar membrane device, recirculated cooling water heat-exchanger rig, acid case, alkali case, described waste water tank, broken cyanide device, filtration unit, be interconnected by lift pump or topping-up pump and connecting tube between bipolar membrane device, be interconnected by pump and connecting tube between described bipolar membrane device and recirculated cooling water heat-exchanger rig, salt water tank and salt water circulating pump is provided with between described filtration unit and bipolar membrane device, described sour case is communicated with the sour room in described bipolar membrane device by acid circulating pump, described alkali case is communicated with the alkali room in described bipolar membrane device by alkali recycle pump.
10. the treatment system of irbesartan amination workshop section according to claim 9 high-concentration salt-containing wastewater treatment process, is characterized in that: described salt water circulating pump exit end is provided with ready-package candle filter, to filter the suspensoid produced in demineralising process.
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Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105293642A (en) * | 2015-11-27 | 2016-02-03 | 福建创源环保有限公司 | Multi-electrode multi-diaphragm electrolytic cell for treating high-salinity industrial wastewater |
| CN105329988A (en) * | 2015-11-27 | 2016-02-17 | 福建创源环保有限公司 | Electrolytic bath for treating high-salt industrial waste water by combining Fenton method with bipolar membrane technology |
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|---|---|---|---|---|
| CN102838240A (en) * | 2012-09-28 | 2012-12-26 | 武汉大学 | Method and system for recovering waste water generated in carbocisteine production |
| CN103073132A (en) * | 2012-12-28 | 2013-05-01 | 中国环境科学研究院 | Process for treating amantadine amination waste water through bipolar membrane electrodialysis process |
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2014
- 2014-10-08 CN CN201410522516.2A patent/CN104230063A/en active Pending
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102838240A (en) * | 2012-09-28 | 2012-12-26 | 武汉大学 | Method and system for recovering waste water generated in carbocisteine production |
| CN103073132A (en) * | 2012-12-28 | 2013-05-01 | 中国环境科学研究院 | Process for treating amantadine amination waste water through bipolar membrane electrodialysis process |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105293642A (en) * | 2015-11-27 | 2016-02-03 | 福建创源环保有限公司 | Multi-electrode multi-diaphragm electrolytic cell for treating high-salinity industrial wastewater |
| CN105329988A (en) * | 2015-11-27 | 2016-02-17 | 福建创源环保有限公司 | Electrolytic bath for treating high-salt industrial waste water by combining Fenton method with bipolar membrane technology |
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Address after: 200437, room 3, building 900, Lane 205, Quyang Road, Shanghai, Hongkou District Applicant after: SHANGHAI BODAN ENVIRONMENTAL ENGINEERING TECHNOLOGY CO., LTD. Address before: 200437, room 3, building 900, Lane 205, Quyang Road, Shanghai, Hongkou District Applicant before: Shanghai Bodan Environmental Engineering Technology Co., Ltd. |
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