WO2019022947A1 - Method for fryer stack water recovery and treatment - Google Patents
Method for fryer stack water recovery and treatment Download PDFInfo
- Publication number
- WO2019022947A1 WO2019022947A1 PCT/US2018/041457 US2018041457W WO2019022947A1 WO 2019022947 A1 WO2019022947 A1 WO 2019022947A1 US 2018041457 W US2018041457 W US 2018041457W WO 2019022947 A1 WO2019022947 A1 WO 2019022947A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- water
- reaction
- acrylamide
- waste water
- fenton reagent
- 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.)
- Ceased
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/722—Oxidation by peroxides
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/441—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/444—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/50—Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/32—Hydrocarbons, e.g. oil
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/38—Organic compounds containing nitrogen
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/32—Nature of the water, waste water, sewage or sludge to be treated from the food or foodstuff industry, e.g. brewery waste waters
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/02—Specific form of oxidant
- C02F2305/026—Fenton's reagent
Definitions
- the present invention relates to a method for reducing and removing the amount of Acrylamide in the water released as steam from the frying of tubers such as potatoes, fryer stack water recovery and treatment, wastewater, water sustainability, and water reuse.
- This invention permits the recovery of fryer stack water having significantly reduced levels of acrylamide.
- the chemical acrylamide has long been used in its polymer form in industrial applications for waste water treatment, enhanced oil recovery, papermaking, flocculants, thickeners, ore processing and permanent-press fabrics.
- Acrylamide precipitates as a white crystalline solid, is odorless, and is highly soluble in water (2155 g/L at 30°C).
- Synonyms for acrylamide include 2-propenamide, ethylene carboxamide, acrylic acid amide, vinyl amide, and propenoic acid amide.
- Acrylamide has a molecular mass of 71.08, a melting point of 84.5°C, and a boiling point of 125°C at 25 mmHg.
- Potatoes typically contain approximately 80% of water by weight. As illustrated in Figure 1, potatoes (106) are washed, peeled and sliced in a washer, peeler and slice operation block (101), fried in a fryer (102) and seasoned to produce a finished product (105). During frying process, water evaporates, which generates low pressure steam (103) along with volatile organic compounds. Steam generated can be condensed using different systems such as vapor absorption chillers and, condenser (104). The fryer stack water and excess steam is currently disposed and not recovered and reused. It has been found that the fryer water condensate shows the presence of Acrylamide and Phenolic compounds.
- the conventional water treatment systems typically include biological treatment processes, membrane processes, resin based technology, and/or ozonation/UV.
- biological treatment processes typically include biological treatment processes, membrane processes, resin based technology, and/or ozonation/UV.
- Such systems are expensive to install and operate and the methods will not treat acrylamide.
- Some of the issues affecting the cost and operation of these systems include fouling of the membranes, leading to higher operating pressure for the membrane systems and lower recoveries of treated water, and more frequent cleaning and replacement of the membranes.
- High cost of equipment and processes is also an issue with conventional water recovery systems.
- Acrylamide is highly hydrophilic in nature which makes it difficult to remove using conventional/membrane systems. These problems have limited the use of conventional systems. Therefore there is a need for a low cost and efficient system to treat recovered water and reduce acrylamide levels to less than 0.1 ppb.
- FIG. 2 illustrates well known prior art methods for making fried potato chips from raw potato stock.
- the raw potatoes which contain about 80% or more water by weight, are first washed and proceed to a peeling step 210. After the skins are peeled from the raw potatoes, the potatoes are then transported to a slicing step 220.
- the thickness of each potato slice at the slicing step 220 is dependent on the desired thickness of the final product.
- An example in the prior art involves slicing the potatoes to a thickness of about 0.04 to about 0.08 inches.
- This cooking step 240 typically involves frying the slices in a continuous fryer at, for example, about 171 °C to about 182°C (340-360°F) for approximately two to three minutes.
- the cooking step generally reduces the moisture level of the chip to less than 2% by weight. For example, a typical fried potato chip exits the fryer with approximately 1 -2% moisture by weight.
- the cooked potato chips are then transported to a seasoning step 250, where seasonings are applied in a rotation drum.
- the seasoned chips proceed to a packaging step 260.
- This packaging step 260 usually involves feeding the seasoned chips to one or more weighers which then direct chips to one or more vertical form, fill, and seal machines for packaging in a flexible package. Once packaged, the product goes into distribution and is purchased by a consumer.
- a fabricated potato chip does not require the peeling step 210, the slicing step 220, or the washing step 230. Instead, fabricated potato chips may start with a dehydrated potato product such as potato flakes. The dehydration of potatoes releases water which is disposed of and not recovered and reused. There is a need to recover the water from the dehydration process.
- the dehydrated potato product is mixed with water and other minor ingredients to form dough. This dough is then sheeted and cut before proceeding to a cooking step.
- the cooking step may involve frying or baking.
- the chips then proceed to a seasoning step and a packaging step.
- the invention provides a method to treat acrylamide in waste water/process water.
- Organic compounds such as phenols and phenolic compounds can be oxidized in the presence of oxidizing compounds like hypo and Fenton reagent.
- Fenton reagent is a product of reaction of Iron Salts (like Ferrous Sulphate-FeS04) and Hydrogen Peroxide (H202). It generates OH* (radical) which has significantly more oxidation power compared to traditional oxidizing agents such as Chlorine.
- the fryer stack water is collected and treated using Fenton reagent such that the Acrylamide levels are reduced to less than 0.1 ppb in the recovered water.
- Figure 1 is a prior art process flow illustrating generation of steam from a fryer stack.
- Figure 2 is a schematic of prior art potato chip processing steps.
- Figure 3 is an exemplary water recovery and treatment system according to an embodiment of the present invention.
- Figures 4a and 4b are an exemplary water recovery and treatment process flow chart according to an embodiment of the present invention.
- Figure 5 is an exemplary water reuse process flow chart according to an embodiment of the present invention.
- the present idea includes an innovative way to treat acrylamide in the waste water/process water.
- Organic compounds such as acrylamide, phenols and phenolic compounds can be oxidized in the presence of oxidizing compounds like hypo, Fenton reagent, etc.
- Fenton reagent is a product from the reaction of Iron Salts (like Ferrous Sulphate-FeS04) and Hydrogen Peroxide (H2O2). It generates OH* (radical) which has significantly more oxidation power compared to traditional oxidizing agents such as
- Equation (1) as in the reaction mechanism shown below illustrates the oxidation of acrylamide with an OH* radical producing CO2, CO, NH3, NO2, NO3, and H2O as byproducts.
- the fryer stack water may be collected and treated using Fenton reagent.
- the levels of acrylamide may be reduced by more than 99% in the water.
- the experiment may be conducted in a lab with waste water samples collected from a unit operation such as a fryer stack located in a manufacturing plant. Base analysis may be conducted to establish contaminants levels. Reagents Ferrous sulphate and Hydrogen Peroxide at different concentration levels may be prepared for the experiments. Preliminary filtration of the waste water may be done using micro/ultra filtration. The filtered water sample may then be treated with Fenton Reagent (FeS04 & H2O2 ) and held in the reactor before passing it through activated carbon filter ("ACF").
- Fenton Reagent FeS04 & H2O2
- ACF treated water may be used to measure acrylamide in the treated sample.
- the Fenton reagent reduces the Acrylamide levels by greater than 99% in the water and in some instances greater than 99.9%. It should be noted the process is simple with few reagents. The process is replicable and reproducible. The simpler process of fewer reagents enables building a lower cost system as compared to conventional treatment systems.
- each one of the potato chip processing steps (the peeling step 210, the slicing step 220, the washing step 230, the cooking step 240, the seasoning step 250, and the packaging step 260) is considered a separate unit operation with regard to the overall process of producing a potato chip food product.
- "waste water”, “recovered water”, or “recovered waste water” means water directly taken or recovered from a unit operation such as a fryer stack.
- "treated water”, “treated recovered water”, or “treated waste water” means water generated from reaction of waste water with a Fenton reagent.
- a first example of the manipulation of a unit operation involves the washing step 230 (illustrated in Figure 2) of potato chips produced by slicing raw potato stock.
- the prior art method of washing slices involves rinsing the chips with water at room temperature.
- the average residence time of each chip in this water rinse in the prior art is typically less than about 60 seconds, depending on the equipment used.
- FIG. 3 illustrates an exemplary water recovery and treatment system according to an embodiment of the present invention.
- the system (300) may include a heat exchanger (310) to reduce process temperatures of steam condensate received from a unit operation such as a fryer stack.
- the waste water or steam condensate may be taken directly from the fryer or as a byproduct from a vapor absorption chiller (not shown).
- the fryer condensate from the chiller or directly from the fryer may be fed to an inlet of the heat exchanger (310).
- the temperature of the fryer condensate is reduced by exchange of heat with cooling water.
- the temperature of the condensate may be reduced from a range of 85°C- 90°C to a range of 25°C to 30°C.
- Output condensate from the heat exchanger (310) may be processed through an oil and grease removal unit (320) using conventional technologies like Oil Skimmer/ API/DAF or membrane systems like MW series membrane or equivalent.
- a multi grade filter may also be used to remove suspended solids (TSS).
- TSS suspended solids
- the waste water from the unit (320) is processed through a microfiltration unit (330) to remove suspended solids.
- the waste water substantially free of oil and grease and suspended solids is then input to a Fenton reactor (340) where acrylamide and Phenolic compounds are removed or reduced through oxidation process.
- the treated water byproduct from the reaction is then passed through an activated carbon filter (350) to remove color and other organics.
- the treated water may be filtered with ultra filtration (360) to remove or reduce suspended solids and turbidity.
- the treated water may then be passed through cartridge filters (370) to remove or reduce micron size particles and to protect reverse osmosis (RO).
- a reverse osmosis (380) may then be performed on the treated water to remove or reduce dissolved solids.
- the treated water may then be disinfected using ultra violet (UV) (390) exposure.
- UV ultra violet
- the treated water from the UV may then be reused in the manufacturing process for various unit operations such as washing, peeling, chilling, heat exchanger and any other unit operations requiring water.
- Reverse Osmosis (RO) treated water may be used as a cooling medium in a cooling tower or other cooling equipment.
- the treated water may also be used as a boiler feed water in a boiler.
- Table 1.0 as shown below demonstrates the reduction of acrylamide levels as the waste water is recovered and treated. As clearly shown, the acrylamide levels have been reduced from 1500 ppb in the fryer stack recovered water to less than 0.1 ppb after the Fenton reaction and after ACF in the final treated water. Table 1.0 shows the Acrylamide levels reduced to 1450 ppb with standard filtering methods (Water CI). Water C2-C6 are treated with different volumes of 5% FeSCn and 30% H2O2. It has been demonstrated that 5 ml of 5% FeSCn and 1.5 ml of 30% H2O2 was the optimal for this particular experiment.
- 5% FeSCn and 30% H2O2 may be added to the Fenton reactor in-situ (at the same time) or separately. In-situ addition enables the OH radical to be available instantly for oxidation of the phenols and phenolic compounds in the fryer stack condensate.
- Table 2.0 as illustrated below shows the reduction of acrylamide for different samples by greater than 99%.
- the level of acrylamide in the final treated water is less than 0.5 ppb.
- the percentage reduction of acrylamide levels from the waste water to the treated water is greater than 99.6%.
- the level of acrylamide in the final treated water is less than 1 ppb.
- the level of acrylamide in the final treated water is less than 0.5 ppb.
- the level of acrylamide in the final treated water is less than 0.1 ppb.
- a method for recovering and treating waste water (400) from a unit operation in a manufacturing process of a food product may be generally described in terms of the following steps: (1) recovering waste water from a unit operation (401);
- the unit operation may be washing, peeling, dehydrating, or the waste water may be taken from a fryer stack directly or after the steam from the fryer is processed through a vapor absorption chiller.
- the fryer condensate may then be passed through a heat exchanger to reduce the temperature in preparation for the reaction of step (404).
- the temperature of the condensate after passing through the heat exchanger may range from 25 ° C to 30 ° C.
- the recovered water from step (401) may then be processed through an oil and grease removal unit (320).
- a reaction between the waste water from step (402) with a Fenton reagent may oxidize acrylamide in the waste water.
- Fenton reagent is a combination product of reaction between Iron Salts (FeS04) and H2O2.
- the concentration of iron salts (FeS04) may range from 1% to 50%.
- the concentration of iron salts (FeS04) may range from 1% to 30%.
- the concentration of H2O2 may range from 10% to 50%.
- the reaction time may range from 1 minute to 120 minutes according to a more preferred exemplary embodiment.
- the reaction time may range from 10 minutes to 60 minutes according to a most preferred exemplary embodiment.
- the acrylamide is oxidized with the hydroxyl radical and therefore the acrylamide levels are reduced in the treated water.
- the pH of the reaction may range from 3 to 6.
- the temperature of the reaction may range from 20°C and 30°C.
- the water after the reaction in step (403) may then be filtered and further processed to remove color, turbidity, micro particles, suspended solids and dissolved solids as illustrated below in steps (405, 406, 407, 408).
- the filtering step (404) may be generally described in terms of the following steps:
- a continuous multi-zone fryer can be used.
- a continuous multi-zone fryer can have two or more hot oil inlets where hot oil is injected after exiting a heat exchanger having an outlet temperature.
- the condensate from the multi-zone fryer may be recovered and treated with the method aforementioned in Figures 4a and 4b and the system of Figure 3.
- FIG. 5 generally illustrates an exemplary water reuse process flow chart according to a preferred embodiment.
- the steam (103) may be recovered and reused as water (108) in the manufacturing process.
- a 20,000 lbs/hr of potatoes (106) may contain 4000 lbs/hr of solids and 16000 lbs/hr. 10% or 1600 lbs/hr of surface water may be added in the washing unit operation (101). The total water that could potentially recovered in 17600 lbs/hr.
- 50 GPM gallons per minute
- 35 GPM may be recovered from the fryer stack and treated for reuse as water (108) in the manufacturing process. Therefore there is at least a 70% reduction in the water requirement for the manufacturing process.
- the amount of water required in the manufacturing is reduced from 50 GPM to 35 GPM.
- Other elements and more than 240 parameters in the treated water were analyzed for compliance with potable standards (USEPA,WHO) and reuse water standards.
- This invention contemplates combining the teachings herein with regard to various unit operation manipulations in order to achieve a desired acrylamide level in the end treated water.
- the combinations used depend on the starting product and the desired end product and can be adjusted by one skilled in the art pursuant to the teachings herein.
- the effect of pH and temperature of the reaction acrylamide with the Fenton Reagent are other factors that may be considered and combined with the teachings herein.
- the present invention method anticipates a wide variety of variations in the basic theme of implementation, but can be generalized as a method for recovering and treating waste water from a unit operation in a manufacturing process of a food product, the method comprising the steps of:
- the present invention anticipates a wide variety of variations in the basic theme of recovering and treating waste water from a unit operation.
- the examples presented previously do not represent the entire scope of possible usages. They are meant to cite a few of the almost limitless possibilities.
- This basic system and method may be augmented with a variety of ancillary embodiments, including but not limited to:
- Fenton reagent is a product of reaction of Iron Salts
- reaction at step c) further comprises a reaction between hydroxyl radical from the Fenton reagent and phenols in the waste water output from the step b).
- reaction at step c) further comprises a reaction between hydroxyl radical from the Fenton reagent and phenolic compounds in the waste water output from the step b).
- An embodiment further comprises reaction of Fenton reagent and acrylamide.
- An embodiment wherein the unit operation is a frying operation and the water from step a) is recovered water from steam in a fryer stack.
- An embodiment wherein the unit operation is a washing or peeling operation.
- An embodiment wherein the food product is potato chip.
- reaction at step c) occurs at pH range between 3 and 6.
- reaction at step c) occurs at temperature range between 20°C and 30°C.
- reaction at step c) has a reaction time ranging from 10 minutes to 60 minutes.
- An embodiment wherein a composition of the Iron Salts ranges from 1% to 30% by volume.
- composition of the H2O2 ranges from 10% to 50% by volume.
- An embodiment wherein the treated from step d) has USEPA,WHO potable water standards.
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
- Physical Water Treatments (AREA)
- General Preparation And Processing Of Foods (AREA)
- Health & Medical Sciences (AREA)
- Toxicology (AREA)
Abstract
Description
Claims
Priority Applications (4)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201880048453.8A CN110944948A (en) | 2017-07-28 | 2018-07-10 | Method for recovering and treating water for fryer chimney |
| CA3069418A CA3069418C (en) | 2017-07-28 | 2018-07-10 | Method for fryer stack water recovery and treatment |
| GB2000880.1A GB2578983B (en) | 2017-07-28 | 2018-07-10 | Method for fryer stack water recovery and treatment |
| ES202090002A ES2759402B2 (en) | 2017-07-28 | 2018-07-10 | Method for recovering and treating water from a deep fryer bowl |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US15/663,282 US10519050B2 (en) | 2017-07-28 | 2017-07-28 | Method for fryer stack recovery and treatment |
| US15/663,282 | 2017-07-28 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO2019022947A1 true WO2019022947A1 (en) | 2019-01-31 |
Family
ID=65040286
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/US2018/041457 Ceased WO2019022947A1 (en) | 2017-07-28 | 2018-07-10 | Method for fryer stack water recovery and treatment |
Country Status (5)
| Country | Link |
|---|---|
| US (1) | US10519050B2 (en) |
| CN (1) | CN110944948A (en) |
| ES (1) | ES2759402B2 (en) |
| GB (1) | GB2578983B (en) |
| WO (1) | WO2019022947A1 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN111392907A (en) * | 2020-04-03 | 2020-07-10 | 贺利氏贵金属技术(中国)有限公司 | Method for treating waste water |
Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4226673A (en) * | 1976-03-15 | 1980-10-07 | Champion International Corporation | Color removal from paper and pulp mill aqueous effluents |
| US6491797B1 (en) * | 1993-11-05 | 2002-12-10 | Florida State University | Methods of oxidizing organic contaminants in aqueous mediums using corona induced reactions |
| US6582605B2 (en) * | 2000-07-07 | 2003-06-24 | Ionics, Incorporated | Method of treating industrial waste waters |
| WO2013044168A1 (en) * | 2011-09-22 | 2013-03-28 | Chevron U.S.A. Inc. | Apparatus and process for treatment of water |
| WO2014066931A1 (en) * | 2012-11-01 | 2014-05-08 | Water Science Technologies Pty Ltd | Process and apparatus for water treatment |
| US20160200605A1 (en) * | 2013-08-22 | 2016-07-14 | Trojan Technologies | Process for treatment of a fluid comprising an oxidizable containment |
| US20170121200A1 (en) * | 2014-05-30 | 2017-05-04 | Znano Llc | Systems for Treating Water |
Family Cites Families (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| BRPI0415046A (en) * | 2003-10-02 | 2006-12-12 | Univ Mississippi | production of biodiesel and other valuable chemicals from wastewater treatment plant waste |
| JP2009530100A (en) * | 2006-03-20 | 2009-08-27 | ビー.ピー.ティー.−バイオ ピュア テクノロジ エルティーディー. | Hybrid membrane module, system and process for treating industrial wastewater |
| CN102515442B (en) * | 2011-12-29 | 2013-06-12 | 蓝星环境工程有限公司 | Treatment method for recycling complex waste water in coal chemical industry |
| CN202482169U (en) * | 2011-12-31 | 2012-10-10 | 上海轻工业研究所有限公司 | Treatment equipment for wastewater of chemicals for daily use |
| HRP20120276A2 (en) * | 2012-03-28 | 2013-09-30 | Višnja Oreščanin | Process and apparatus for electrochemical treatment of industrial wastewater and drinking water |
| CN102671706A (en) * | 2012-05-22 | 2012-09-19 | 陕西海安实业有限责任公司 | Efficient Fenton-like system catalyst and preparation method thereof |
| CN103641275B (en) * | 2013-12-13 | 2016-01-06 | 广西大学 | The treatment process of brewing industry sewage and equipment |
| WO2016037149A1 (en) * | 2014-09-04 | 2016-03-10 | Clean Chemistry, Inc. | Method of water treatment utilizing a peracetate oxidant solution |
-
2017
- 2017-07-28 US US15/663,282 patent/US10519050B2/en active Active
-
2018
- 2018-07-10 ES ES202090002A patent/ES2759402B2/en active Active
- 2018-07-10 WO PCT/US2018/041457 patent/WO2019022947A1/en not_active Ceased
- 2018-07-10 CN CN201880048453.8A patent/CN110944948A/en active Pending
- 2018-07-10 GB GB2000880.1A patent/GB2578983B/en active Active
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4226673A (en) * | 1976-03-15 | 1980-10-07 | Champion International Corporation | Color removal from paper and pulp mill aqueous effluents |
| US6491797B1 (en) * | 1993-11-05 | 2002-12-10 | Florida State University | Methods of oxidizing organic contaminants in aqueous mediums using corona induced reactions |
| US6582605B2 (en) * | 2000-07-07 | 2003-06-24 | Ionics, Incorporated | Method of treating industrial waste waters |
| WO2013044168A1 (en) * | 2011-09-22 | 2013-03-28 | Chevron U.S.A. Inc. | Apparatus and process for treatment of water |
| WO2014066931A1 (en) * | 2012-11-01 | 2014-05-08 | Water Science Technologies Pty Ltd | Process and apparatus for water treatment |
| US20160200605A1 (en) * | 2013-08-22 | 2016-07-14 | Trojan Technologies | Process for treatment of a fluid comprising an oxidizable containment |
| US20170121200A1 (en) * | 2014-05-30 | 2017-05-04 | Znano Llc | Systems for Treating Water |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN111392907A (en) * | 2020-04-03 | 2020-07-10 | 贺利氏贵金属技术(中国)有限公司 | Method for treating waste water |
Also Published As
| Publication number | Publication date |
|---|---|
| GB2578983B (en) | 2021-12-29 |
| US10519050B2 (en) | 2019-12-31 |
| ES2759402A2 (en) | 2020-05-08 |
| CA3069418A1 (en) | 2019-01-31 |
| ES2759402R1 (en) | 2020-05-14 |
| ES2759402B2 (en) | 2021-03-15 |
| CN110944948A (en) | 2020-03-31 |
| GB2578983A (en) | 2020-06-03 |
| GB202000880D0 (en) | 2020-03-04 |
| US20190031541A1 (en) | 2019-01-31 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| Murray et al. | Removal of NOM from drinking water: Fenton’s and photo-Fenton’s processes | |
| CN104150721B (en) | A kind of recycling processing method for foodstuff pickling waste water | |
| Houshyar et al. | Influence of ozonation process on characteristics of pre-alkalized tannery effluents | |
| Ike et al. | Activation of persulfate at waste heat temperatures for humic acid degradation | |
| Agbaba et al. | Oxidation of natural organic matter with processes involving O 3, H 2 O 2 and UV light: formation of oxidation and disinfection by-products | |
| JPWO2008108506A1 (en) | Method for treating black liquor containing no sulfide | |
| WO2013146852A1 (en) | Method for membrane-treating formaldehyde-containing discharge water | |
| JPH0790219B2 (en) | Pure water production apparatus and production method | |
| WO2003022751B1 (en) | Method of multi-stage reverse osmosis treatment | |
| US10519050B2 (en) | Method for fryer stack recovery and treatment | |
| JP5527473B2 (en) | Membrane treatment method for formaldehyde-containing wastewater | |
| JP2014083521A (en) | Treatment method of aldehyde-containing drainage water and treatment apparatus of aldehyde-containing drainage water | |
| CA3069418C (en) | Method for fryer stack water recovery and treatment | |
| JP2013193003A (en) | Treatment method and treatment system of plant wastewater | |
| Drikas et al. | Removal of natural organic matter-a fresh approach | |
| Ochando-Pulido et al. | Experimental design optimization of reverse osmosis purification of pretreatedolive mill wastewater | |
| CN110563188B (en) | Method and system for preparing drinking weak alkaline water and strontium-rich electrolyte raw material water from salt-making distilled water | |
| Campos-Flores et al. | Passion-fruit shell biomass as adsorbent material to remove chromium III from contaminated aqueous mediums | |
| Souza et al. | Comparative study of various advanced oxidation processes for the treatment of tannery wastewater | |
| JP5348297B1 (en) | Method and apparatus for treating formaldehyde-containing wastewater | |
| Shokoohi et al. | Evaluation of US/S2O8-2 compilative process performance in the removal of Erythrosine B dye from aqueous solution | |
| Alshamsi et al. | UV-ClO2 assisted decolorization of methylene blue | |
| EP3793947B1 (en) | A process to recycle water condensate from co2 off gas stream | |
| Garrido et al. | Reconditioning of wash water for the fresh-cut industry | |
| Li et al. | O3-assisted UV-Fenton treatment of refining reverse osmosis water: optimization of process conditions by response surface methodology |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| 121 | Ep: the epo has been informed by wipo that ep was designated in this application |
Ref document number: 18838424 Country of ref document: EP Kind code of ref document: A1 |
|
| ENP | Entry into the national phase |
Ref document number: 3069418 Country of ref document: CA |
|
| ENP | Entry into the national phase |
Ref document number: 202000880 Country of ref document: GB Kind code of ref document: A Free format text: PCT FILING DATE = 20180710 |
|
| NENP | Non-entry into the national phase |
Ref country code: DE |
|
| 122 | Ep: pct application non-entry in european phase |
Ref document number: 18838424 Country of ref document: EP Kind code of ref document: A1 |

