CN1541757A - E-Fenton oxidation technique of dirty blocking agent in reverse osmosis concentrating liquid - Google Patents

E-Fenton oxidation technique of dirty blocking agent in reverse osmosis concentrating liquid Download PDF

Info

Publication number
CN1541757A
CN1541757A CNA2003101084542A CN200310108454A CN1541757A CN 1541757 A CN1541757 A CN 1541757A CN A2003101084542 A CNA2003101084542 A CN A2003101084542A CN 200310108454 A CN200310108454 A CN 200310108454A CN 1541757 A CN1541757 A CN 1541757A
Authority
CN
China
Prior art keywords
reverse osmosis
concentrated solution
solution
scale inhibitor
coagulation
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CNA2003101084542A
Other languages
Chinese (zh)
Other versions
CN1235668C (en
Inventor
杨庆峰
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Shanghai Jiaotong University
Original Assignee
Shanghai Jiaotong University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Shanghai Jiaotong University filed Critical Shanghai Jiaotong University
Priority to CN 200310108454 priority Critical patent/CN1235668C/en
Publication of CN1541757A publication Critical patent/CN1541757A/en
Application granted granted Critical
Publication of CN1235668C publication Critical patent/CN1235668C/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

The electric Fenton oxidation process for processing scale inhibitor in reverse osmosis concentrated liquid adopts anode of iron plate and cathode of porous graphite and ventilated with air pump and processes reverse osmosis concentrated liquid through electrolyzing in stirring, stirring coagulation via adding aluminum sulfate and filtering the coagulated solution. Bivalent iron ion produced intelligent the electric Fenton process is made to react with hydrogen peroxide to produce strong oxidizing free hydroxy radical oxidizing and destructing the scale inhibitor; and the subsequent coagulation separates out scaling salt to lower the scaling trend, so that the concentrated liquid may be utilized as influent water to raise the water recovering rate of reverse osmosis system.

Description

electro-Fenton oxidation method of scale inhibitor in reverse osmosis concentrated solution
The technical field is as follows:
the invention relates to an electro-Fenton (Fenton) oxidation method for scale inhibitors in reverse osmosis concentrated solution, which adopts the electro-Fenton method to reduce the scaling tendency of the reverse osmosis concentrated solution, improve the water recovery rate of a reverse osmosis system and realize the reutilization of concentrated solution resources. Belongs to the technical field of wastewater treatment in environmental science.
Background art:
reverse Osmosis (RO) desalination is widely used in the industrial fields of brackish water and seawater desalination, medicine production, high-purity water in electronic industry, water for beverages, chemical production and the like. Compared with distillation desalination, reverse osmosis has the outstanding advantages of low energy consumption, simple and convenient operation, no discharge of regenerated waste liquid, small system floor area, economic operation cost and the like. With the improvement of membrane preparation technology, the development of energy recovery systems, the improvement of pretreatment technology and the wide applicability of high and low salinity influent water, the reverse osmosis desalination cost is obviously reduced year by year, and the competitiveness of reverse osmosis technology on economy and technology is continuously enhanced, so that the reverse osmosis desalination technology becomes one of the leading high and new technologies in the field of desalination in the 21 st century.
The fouling of membranes is a very troublesome problem in the long run of reverse osmosis systems, and its presence causes a large reduction in the water yield of reverse osmosis units, limiting the wider application of this technology. In order to overcome the scaling problem, the reverse osmosis system generally adds a scale inhibitor into the inlet water during operation so as to maintain the scaling ions at a high supersaturation degree without scaling, thereby improving the recovery rate of water.
After the recovery rate of the reverse osmosis system reaches a certain degree, if the recovery rate is increased, the scale forming ions in the solution are highly supersaturated, the scale forming ions cannot be maintained in a non-scaling state by the scale inhibitor, and the scale forming ions are scaled and separated out on a membrane, so that only concentrated solution is discharged. There will be a discharge of the final concentrate even if concentrate recycling techniques are employed. The final discharge liquid of reverse osmosis is not well utilized at present, and is generally directly discharged, so that the waste of water resources is caused. In fact, the reverse osmosis influent is also highly water-conditioned due to the severe pretreatment. The concentrated solution contains high salt content, especially Ca2+、Mg2+、HCO3 -The plasma scaling ions have high concentration and a large scaling tendency, i.e., a high LSI (Langeri saturation index), and are prone to scale and cannot be used continuously.
The invention content is as follows:
the invention aims to provide an electro-Fenton oxidation method of a scale inhibitor in a reverse osmosis concentrated solution aiming at the defects of the prior art, which can reduce the scaling tendency of the reverse osmosis concentrated solution and ensure that the reverse osmosis concentrated solution is reused as inlet water.
In order to achieve the purpose, the technical scheme of the invention adopts an electrochemical oxidation method, namely an electro-Fenton method, to treat the reverse osmosis concentrated solution, and ferrous ions (Fe) generated by the electrochemical process are utilized2+) And hydrogen peroxide (H)2O2) Strong oxidant generated by the reaction, namely hydroxyl radical (OH), is used for oxidizing and destroying the scale inhibitor in the reverse osmosis concentrated solution to destabilize high supersaturation scale-forming ions in the solution, and then, the solution is coagulated to enable the scale-forming salts in the concentrated solution to be like CaCO3And the scaling tendency of the solution is reduced by precipitation, so that the concentrated solution can be reused as inlet water, and the water recovery rate of the reverse osmosis system is improved.
In the electro-Fenton method, the anode adopts an iron plate, the cathode adopts porous graphite, the cathode is aerated by air pump, and the gas flow is 0.03-0.12m3And h, electrolyzing the reverse osmosis concentrated solution at the electrolysis voltage of 5V for 30-60 minutes under stirring.
During electrolysis, iron is dissolved at the anode to produce Fe2+H is produced by the reaction of the formula (1) at the cathode2O2Electrically generated Fe2+And H2O2The Fenton reaction of the formula (2) is carried out, strong oxidation-OH&is generated in situ, the standard electrode potential of the Fenton reaction is 2.8V, and almost all scale inhibitor organic matters can be oxidized.
(1)
(2)
After the electrolytic treatment, the antisludging agent in the concentrated solution is destroyed, and the scaling ions in the highly supersaturated concentrated solution automatically generate crystal particles to be suspended in the solution, at the moment, the concentrated solution becomes turbid. In order to remove the suspended scaling particles efficiently, the invention adopts a coagulation method: namely, after the electrolysis, 200mg/L of aluminum sulfate was added to carry out coagulation. During coagulation, the solution is firstly stirred and coagulated for half a minute at 300 revolutions per minute to fully mix the coagulant and the solution, then the stirring speed is reduced to 50 revolutions per minute, and coagulation is carried out for 5 minutes to fully grow the formed alum floc. After the mixing and coagulation, the solution is filtered to remove the precipitated alum floc, and the treated reverse osmosis concentrated solution is obtained, the scaling tendency of the concentrated solution is greatly reduced, and the concentrated solution can be reused as the inlet water of a reverse osmosis system.
The ion concentration of the treated reverse osmosis concentrated solution is analyzed, and LSI (Langelier Langerel saturation index) value is calculated, and the result shows that the scaling tendency of the solution is greatly reduced and can be reduced to about 0.6 LSI.
The reverse osmosis concentrated solution adopted by the method has high salt concentration and good conductivity, and the energy consumption can be reduced when the reverse osmosis concentrated solution is treated by an electrolytic method. OH generated by electro-Fenton has strong oxidability, the efficiency of treating the scale inhibitor is high, the speed is high, the scale inhibitor in the concentrated solution can be oxidized, and the scaling tendency of the concentrated solution is greatly reduced; automatic generation of Fe during the process2+And H2O2,No chemical reagent is added, so that the cost is low; the treatment process is environment-friendly, no harmful substances are discharged, the treated concentrated solution can be reused as inlet water, the concentrated solution is recycled, and the water recovery rate of the reverse osmosis system is improved.
Description of the drawings:
FIG. 1 shows the results of the treatment in example 1 of the present invention.
FIG. 2 shows the results of the treatment in example 2 of the present invention.
The specific implementation mode is as follows:
the technical solution of the present invention is further described below with reference to the accompanying drawings and examples.
Example 1
0.72 g NaHCO was weighed31.18 g of CaCl20.22 g MgSO4·7H2O, 0.228 g NaNO3Placed in 800 ml of distilled water to prepare a concentrated solution having an initial pH of 7.8 and an initial LSI0Is 1.86. Adding the scale inhibitor, wherein the concentration of the scale inhibitor is 7 mg/L.
The electrolytic anode adopts an iron plate, the cathode adopts porous graphite, and the areas of the two electrodes are both 45cm2. The cathode is aerated by air pump with air flow of 0.12m3The electrolysis voltage is 5V, the time is 30 minutes, and the solution is electrolyzed under stirring. And adding 200mg/L aluminum sulfate after electrolysis for coagulation and filtration to obtain a treated concentrated solution. For the coagulation, the coagulation was carried out at 300 rpm for half a minute, followed by 50 rpm for 5 minutes.
electro-Fenton Oxidation of 8 different commercial Scale inhibitors, designated by letters A to H, containing-COOH, -PO3H2,-OH,-SO3H, -COOR and the like.
FIG. 1 shows the results of electro-Fenton treatment of 8 kinds of scale inhibitors, from which LSI of the concentrated solution is shownfThe reduction to 0.61 indicates that the scale inhibitor is oxidized, and the treatment results of 8 scale inhibitors are basically the same, which indicates that OH-oxidizes the scale inhibitor with high efficiency and no selectivity, so the invention has universality for the treatment of the scale inhibitor.
Example 2
1.712 g NaHCO were weighed32.458 g of CaCl20.414 g MgSO4·7H2O, 0.428 g NaNO3Placed in 800 ml of distilled water to prepare a concentrated solution having an initial pH of 7.8 and an initial LSI0Is 2.44. 3 kinds of scale inhibitors A, B and C were added to the solution for electrolysis, and the concentrations were 21 mg/L.
The electrolytic anode adopts an iron plate, the cathode adopts porous graphite, and the areas of the two electrodes are both 45cm2. The cathode is aerated by air pump with air flow of 0.12m3The electrolysis voltage is 5V, the time is 30 minutes, and the solution is electrolyzed under stirring. And adding 200mg/L aluminum sulfate after electrolysis for coagulation and filtration to obtain a treated concentrated solution. For the coagulation, the coagulation was carried out at 300 rpm for half a minute, followed by 50 rpm for 5 minutes.
The results of the electrolysis are shown in FIG. 2. As can be seen from the figure, LSI of concentrated solutionfThe LSI value of the scaling tendency is reduced to 0.59 by 76 percent, and the treatment effect is obviousAnd the treatment results of the 3 kinds of scale inhibitors are basically the same. This further shows that the efficiency is high and thereis no selectivity when OH.O. is oxidized scale inhibitor, and the method of the invention has broad applicability.
Example 3
0.72 g NaHCO was weighed31.18 g of CaCl20.22 g MgSO4·7H2O, 0.228 g NaNO3Placed in 800 ml of distilled water to prepare a concentrated solution having an initial pH of 7.8 and an initial LSI0Is 1.86. Adding scale inhibitor B, and electrolyzing at 3 concentrations of 7mg/L, 21mg/L and 35mg/L respectively.
The electrolytic anode adopts an iron plate, the cathode adopts porous graphite, and the areas of the two electrodes are both 45cm2. The cathode is aerated by air pump, and the air flow is 0.03m3The electrolysis voltage is 5V, the time is 30 minutes, and the solution is electrolyzed under stirring. And adding 200mg/L aluminum sulfate after electrolysis for coagulation and filtration to obtain a treated concentrated solution. For the coagulation, the coagulation was carried out at 300 rpm for half a minute, followed by 50 rpm for 5 minutes.
Calculating to obtain LSI of the treated concentrated solution by solution ion analysisfThe values were reduced to 0.58, 0.62 and 0.70, respectively, indicating that the fouling tendency of the solution has been greatly reduced. Meanwhile, the change of the concentration of the scale inhibitor has little influence on the effect of electro-Fenton oxidation treatment, which shows that the oxidation capacity of OH&generated in the process is very strong.
Example 4
0.72 g NaHCO was weighed31.18 g of CaCl20.22 g MgSO4·7H2O, 0.228 g NaNO3Placed in 800 ml of distilled water to prepare a concentrated solution having an initial pH of 7.8 and an initial LSI0Is 1.86. Adding scale inhibitor C withconcentration of 7 mg/L.
The electrolytic anode adopts an iron plate, the cathode adopts porous graphite, and the areas of the two electrodes are both 45cm2. The cathode is aerated by air pump, and the air flow is 0.03m3The electrolysis was carried out with stirring at an electrolysis voltage of 5V for 30 minutes and 60 minutes, respectively. And adding 200mg/L aluminum sulfate after electrolysis for coagulation and filtration to obtain a treated concentrated solution. During coagulationCoagulation was performed at 300 rpm for half a minute, followed by coagulation at 50 rpm for 5 minutes.
Calculating to obtain LSI of the treated concentrated solution by solution ion analysisfThe reduction to 0.61 and 0.57, respectively, indicates that the fouling tendency of the solution has been greatly reduced. Meanwhile, the effect of the electro-Fenton oxidation treatment is not greatly influenced by the electrolysis time, which shows that the oxidation capability of OH&generated in the process is very strong, and the oxidation reaction of the scale inhibitor is basically completed within 30 minutes.

Claims (1)

1. The electro-Fenton oxidation method of scale inhibitor in reverse osmosis concentrated solution is characterized in that an electro-Fenton method is adopted to oxidize the scale inhibitor containing-COOH and-PO3H2,-OH,-SO3Treating reverse osmosis concentrated solution of scale inhibitor containing H-COOR group with anode made of iron plate, cathode made of porous graphite, air pumped by air pump and gas flow rate of 0.03-0.12m3And h, electrolyzing the reverse osmosis concentrated solution under stirring, wherein the electrolysis voltage is 5V, the time is 30-60 minutes, adding 200mg/L aluminum sulfate for coagulation after theelectrolysis is finished, stirring and coagulating the solution at 300 revolutions per minute, fully mixing the coagulant and the solution, reducing the stirring speed to 50 revolutions per minute for coagulation for 5 minutes, and filtering the solution after the coagulation is finished to obtain the treated reverse osmosis concentrated solution.
CN 200310108454 2003-11-06 2003-11-06 E-Fenton oxidation technique of dirty blocking agent in reverse osmosis concentrating liquid Expired - Fee Related CN1235668C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN 200310108454 CN1235668C (en) 2003-11-06 2003-11-06 E-Fenton oxidation technique of dirty blocking agent in reverse osmosis concentrating liquid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN 200310108454 CN1235668C (en) 2003-11-06 2003-11-06 E-Fenton oxidation technique of dirty blocking agent in reverse osmosis concentrating liquid

Publications (2)

Publication Number Publication Date
CN1541757A true CN1541757A (en) 2004-11-03
CN1235668C CN1235668C (en) 2006-01-11

Family

ID=34334678

Family Applications (1)

Application Number Title Priority Date Filing Date
CN 200310108454 Expired - Fee Related CN1235668C (en) 2003-11-06 2003-11-06 E-Fenton oxidation technique of dirty blocking agent in reverse osmosis concentrating liquid

Country Status (1)

Country Link
CN (1) CN1235668C (en)

Cited By (37)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006012691A1 (en) * 2004-08-04 2006-02-09 U.S. Filter Wastewater Group, Inc. Chemical and process for cleaning membranes
CN100415659C (en) * 2006-09-21 2008-09-03 上海交通大学 Coagulating removing method of calcium sulfate fouling in reverse osmosis concentrated liquid
US7938966B2 (en) 2002-10-10 2011-05-10 Siemens Water Technologies Corp. Backwash method
US8048306B2 (en) 1996-12-20 2011-11-01 Siemens Industry, Inc. Scouring method
US8182687B2 (en) 2002-06-18 2012-05-22 Siemens Industry, Inc. Methods of minimising the effect of integrity loss in hollow fibre membrane modules
US8268176B2 (en) 2003-08-29 2012-09-18 Siemens Industry, Inc. Backwash
US8287743B2 (en) 2007-05-29 2012-10-16 Siemens Industry, Inc. Membrane cleaning with pulsed airlift pump
US8293098B2 (en) 2006-10-24 2012-10-23 Siemens Industry, Inc. Infiltration/inflow control for membrane bioreactor
US8318028B2 (en) 2007-04-02 2012-11-27 Siemens Industry, Inc. Infiltration/inflow control for membrane bioreactor
US8377305B2 (en) 2004-09-15 2013-02-19 Siemens Industry, Inc. Continuously variable aeration
US8382981B2 (en) 2008-07-24 2013-02-26 Siemens Industry, Inc. Frame system for membrane filtration modules
US8496828B2 (en) 2004-12-24 2013-07-30 Siemens Industry, Inc. Cleaning in membrane filtration systems
US8506806B2 (en) 2004-09-14 2013-08-13 Siemens Industry, Inc. Methods and apparatus for removing solids from a membrane module
US8512568B2 (en) 2001-08-09 2013-08-20 Siemens Industry, Inc. Method of cleaning membrane modules
US8518256B2 (en) 2001-04-04 2013-08-27 Siemens Industry, Inc. Membrane module
US8758622B2 (en) 2004-12-24 2014-06-24 Evoqua Water Technologies Llc Simple gas scouring method and apparatus
US8758621B2 (en) 2004-03-26 2014-06-24 Evoqua Water Technologies Llc Process and apparatus for purifying impure water using microfiltration or ultrafiltration in combination with reverse osmosis
US8790515B2 (en) 2004-09-07 2014-07-29 Evoqua Water Technologies Llc Reduction of backwash liquid waste
US8808540B2 (en) 2003-11-14 2014-08-19 Evoqua Water Technologies Llc Module cleaning method
US8858796B2 (en) 2005-08-22 2014-10-14 Evoqua Water Technologies Llc Assembly for water filtration using a tube manifold to minimise backwash
CN104096483A (en) * 2014-08-06 2014-10-15 艾欧史密斯(上海)水处理产品有限公司 Membrane element, device and water processing method using the membrane element
US8956464B2 (en) 2009-06-11 2015-02-17 Evoqua Water Technologies Llc Method of cleaning membranes
US9022224B2 (en) 2010-09-24 2015-05-05 Evoqua Water Technologies Llc Fluid control manifold for membrane filtration system
CN105692971A (en) * 2016-03-18 2016-06-22 沈阳飞机工业(集团)有限公司 Method for treating aluminum alloy chemical milling cleaning liquid through electro-Fenton oxidization
US9533261B2 (en) 2012-06-28 2017-01-03 Evoqua Water Technologies Llc Potting method
US9604166B2 (en) 2011-09-30 2017-03-28 Evoqua Water Technologies Llc Manifold arrangement
US9675938B2 (en) 2005-04-29 2017-06-13 Evoqua Water Technologies Llc Chemical clean for membrane filter
US9764288B2 (en) 2007-04-04 2017-09-19 Evoqua Water Technologies Llc Membrane module protection
US9764289B2 (en) 2012-09-26 2017-09-19 Evoqua Water Technologies Llc Membrane securement device
US9815027B2 (en) 2012-09-27 2017-11-14 Evoqua Water Technologies Llc Gas scouring apparatus for immersed membranes
US9914097B2 (en) 2010-04-30 2018-03-13 Evoqua Water Technologies Llc Fluid flow distribution device
US9925499B2 (en) 2011-09-30 2018-03-27 Evoqua Water Technologies Llc Isolation valve with seal for end cap of a filtration system
US9962865B2 (en) 2012-09-26 2018-05-08 Evoqua Water Technologies Llc Membrane potting methods
US10322375B2 (en) 2015-07-14 2019-06-18 Evoqua Water Technologies Llc Aeration device for filtration system
US10427102B2 (en) 2013-10-02 2019-10-01 Evoqua Water Technologies Llc Method and device for repairing a membrane filtration module
CN111675354A (en) * 2020-06-01 2020-09-18 北京朗新明环保科技有限公司 Method for treating circulating sewage of power plant by using electrochemical crystallization granulation system
CN115215493A (en) * 2021-04-20 2022-10-21 国家能源投资集团有限责任公司 Method and device for treating scale inhibitor in membrane concentrated solution

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101734779B (en) * 2008-11-17 2013-03-13 杭州生源医疗保健技术开发有限公司 Method for preparing Fenton reagent on site for treating waste water

Cited By (50)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8048306B2 (en) 1996-12-20 2011-11-01 Siemens Industry, Inc. Scouring method
US8518256B2 (en) 2001-04-04 2013-08-27 Siemens Industry, Inc. Membrane module
US8512568B2 (en) 2001-08-09 2013-08-20 Siemens Industry, Inc. Method of cleaning membrane modules
US8182687B2 (en) 2002-06-18 2012-05-22 Siemens Industry, Inc. Methods of minimising the effect of integrity loss in hollow fibre membrane modules
US7938966B2 (en) 2002-10-10 2011-05-10 Siemens Water Technologies Corp. Backwash method
US8268176B2 (en) 2003-08-29 2012-09-18 Siemens Industry, Inc. Backwash
US8808540B2 (en) 2003-11-14 2014-08-19 Evoqua Water Technologies Llc Module cleaning method
US8758621B2 (en) 2004-03-26 2014-06-24 Evoqua Water Technologies Llc Process and apparatus for purifying impure water using microfiltration or ultrafiltration in combination with reverse osmosis
WO2006012691A1 (en) * 2004-08-04 2006-02-09 U.S. Filter Wastewater Group, Inc. Chemical and process for cleaning membranes
US8790515B2 (en) 2004-09-07 2014-07-29 Evoqua Water Technologies Llc Reduction of backwash liquid waste
US8506806B2 (en) 2004-09-14 2013-08-13 Siemens Industry, Inc. Methods and apparatus for removing solids from a membrane module
US8377305B2 (en) 2004-09-15 2013-02-19 Siemens Industry, Inc. Continuously variable aeration
US8758622B2 (en) 2004-12-24 2014-06-24 Evoqua Water Technologies Llc Simple gas scouring method and apparatus
US8496828B2 (en) 2004-12-24 2013-07-30 Siemens Industry, Inc. Cleaning in membrane filtration systems
US9675938B2 (en) 2005-04-29 2017-06-13 Evoqua Water Technologies Llc Chemical clean for membrane filter
US8894858B1 (en) 2005-08-22 2014-11-25 Evoqua Water Technologies Llc Method and assembly for water filtration using a tube manifold to minimize backwash
US8858796B2 (en) 2005-08-22 2014-10-14 Evoqua Water Technologies Llc Assembly for water filtration using a tube manifold to minimise backwash
CN100415659C (en) * 2006-09-21 2008-09-03 上海交通大学 Coagulating removing method of calcium sulfate fouling in reverse osmosis concentrated liquid
US8293098B2 (en) 2006-10-24 2012-10-23 Siemens Industry, Inc. Infiltration/inflow control for membrane bioreactor
US8623202B2 (en) 2007-04-02 2014-01-07 Siemens Water Technologies Llc Infiltration/inflow control for membrane bioreactor
US8318028B2 (en) 2007-04-02 2012-11-27 Siemens Industry, Inc. Infiltration/inflow control for membrane bioreactor
US9764288B2 (en) 2007-04-04 2017-09-19 Evoqua Water Technologies Llc Membrane module protection
US8622222B2 (en) 2007-05-29 2014-01-07 Siemens Water Technologies Llc Membrane cleaning with pulsed airlift pump
US9573824B2 (en) 2007-05-29 2017-02-21 Evoqua Water Technologies Llc Membrane cleaning with pulsed airlift pump
US10507431B2 (en) 2007-05-29 2019-12-17 Evoqua Water Technologies Llc Membrane cleaning with pulsed airlift pump
US8287743B2 (en) 2007-05-29 2012-10-16 Siemens Industry, Inc. Membrane cleaning with pulsed airlift pump
US8840783B2 (en) 2007-05-29 2014-09-23 Evoqua Water Technologies Llc Water treatment membrane cleaning with pulsed airlift pump
US8372276B2 (en) 2007-05-29 2013-02-12 Siemens Industry, Inc. Membrane cleaning with pulsed airlift pump
US9206057B2 (en) 2007-05-29 2015-12-08 Evoqua Water Technologies Llc Membrane cleaning with pulsed airlift pump
US9023206B2 (en) 2008-07-24 2015-05-05 Evoqua Water Technologies Llc Frame system for membrane filtration modules
US8382981B2 (en) 2008-07-24 2013-02-26 Siemens Industry, Inc. Frame system for membrane filtration modules
US8956464B2 (en) 2009-06-11 2015-02-17 Evoqua Water Technologies Llc Method of cleaning membranes
US10441920B2 (en) 2010-04-30 2019-10-15 Evoqua Water Technologies Llc Fluid flow distribution device
US9914097B2 (en) 2010-04-30 2018-03-13 Evoqua Water Technologies Llc Fluid flow distribution device
US9022224B2 (en) 2010-09-24 2015-05-05 Evoqua Water Technologies Llc Fluid control manifold for membrane filtration system
US9630147B2 (en) 2010-09-24 2017-04-25 Evoqua Water Technologies Llc Fluid control manifold for membrane filtration system
US9925499B2 (en) 2011-09-30 2018-03-27 Evoqua Water Technologies Llc Isolation valve with seal for end cap of a filtration system
US9604166B2 (en) 2011-09-30 2017-03-28 Evoqua Water Technologies Llc Manifold arrangement
US10391432B2 (en) 2011-09-30 2019-08-27 Evoqua Water Technologies Llc Manifold arrangement
US9533261B2 (en) 2012-06-28 2017-01-03 Evoqua Water Technologies Llc Potting method
US9764289B2 (en) 2012-09-26 2017-09-19 Evoqua Water Technologies Llc Membrane securement device
US9962865B2 (en) 2012-09-26 2018-05-08 Evoqua Water Technologies Llc Membrane potting methods
US9815027B2 (en) 2012-09-27 2017-11-14 Evoqua Water Technologies Llc Gas scouring apparatus for immersed membranes
US10427102B2 (en) 2013-10-02 2019-10-01 Evoqua Water Technologies Llc Method and device for repairing a membrane filtration module
US11173453B2 (en) 2013-10-02 2021-11-16 Rohm And Haas Electronic Materials Singapores Method and device for repairing a membrane filtration module
CN104096483A (en) * 2014-08-06 2014-10-15 艾欧史密斯(上海)水处理产品有限公司 Membrane element, device and water processing method using the membrane element
US10322375B2 (en) 2015-07-14 2019-06-18 Evoqua Water Technologies Llc Aeration device for filtration system
CN105692971A (en) * 2016-03-18 2016-06-22 沈阳飞机工业(集团)有限公司 Method for treating aluminum alloy chemical milling cleaning liquid through electro-Fenton oxidization
CN111675354A (en) * 2020-06-01 2020-09-18 北京朗新明环保科技有限公司 Method for treating circulating sewage of power plant by using electrochemical crystallization granulation system
CN115215493A (en) * 2021-04-20 2022-10-21 国家能源投资集团有限责任公司 Method and device for treating scale inhibitor in membrane concentrated solution

Also Published As

Publication number Publication date
CN1235668C (en) 2006-01-11

Similar Documents

Publication Publication Date Title
CN1541757A (en) E-Fenton oxidation technique of dirty blocking agent in reverse osmosis concentrating liquid
WO2002026639A1 (en) Method and apparatus for clarification of water
CN110272158A (en) A kind of high salt, high organic matter and high rigidity wastewater treatment method
CN100336737C (en) Method of removing ammonia nitrogen in water by using electrodialysis
JP5498477B2 (en) Active metal salt flocculant and method for producing the same
CN113307438A (en) Treatment method of nickel-cobalt smelting heavy metal wastewater
CN113003846A (en) Zero-emission treatment process and system for sewage with high salt content and high COD (chemical oxygen demand)
CN105084631B (en) A kind of handling process of resin regeneration waste water
CN111320316A (en) Landfill leachate membrane concentrated solution treatment method
CN103951017A (en) Method for treating cyanogen-containing copper-containing electroplating wastewater by electrolysis and recycling copper
TWI637917B (en) Fluoride removal method of flue-gas desulfurization wastewater and fluoride removal system thereof
CN111233208A (en) Desulfurization waste water resource recovery system
CN210915600U (en) Recycling device of RO strong brine
CN201785261U (en) Treatment and recovery device for aluminum oxidation rinsing wastewater
CN207108721U (en) Mercury-containing waste water advanced treating zero-emission system
CN215102340U (en) Low-cost resourceful treatment system of coal industry high salt waste water
CN211896410U (en) Desulfurization waste water resource recovery system
WO2021223369A1 (en) Chemical-free electric method combined treatment process system and method for circulating water of thermal power plant
CN113845267A (en) Electric flocculation treatment method for natural bubble gas production wastewater
CN100475320C (en) Internal electrolyte destruction of scale inhibitor in reverse osmosis concentrate
CN114644425A (en) Treatment method of cellulose ether industrial wastewater with high salt content and high COD value
JP2012196657A (en) Treatment method of wastewater containing phenols
CN1089315C (en) Method for purification of waste water
CN111908718A (en) Advanced treatment method of garbage penetrating fluid
CN109437451A (en) It is a kind of for oil-containing and surface active agent wastewater can reuse equipment and technique

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
C19 Lapse of patent right due to non-payment of the annual fee
CF01 Termination of patent right due to non-payment of annual fee