CN101857319A - Method for recycling protein from protein-contained waste water - Google Patents
Method for recycling protein from protein-contained waste water Download PDFInfo
- Publication number
- CN101857319A CN101857319A CN 201010148143 CN201010148143A CN101857319A CN 101857319 A CN101857319 A CN 101857319A CN 201010148143 CN201010148143 CN 201010148143 CN 201010148143 A CN201010148143 A CN 201010148143A CN 101857319 A CN101857319 A CN 101857319A
- Authority
- CN
- China
- Prior art keywords
- acid
- protein
- waste water
- proteinic wastewater
- contain
- 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.)
- Pending
Links
Landscapes
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
The invention discloses a method for recycling protein from protein-contained waste water, which is characterized in that: the protein-contained waste water is firstly and primarily purified and decontaminated, after adding acid and/or alkali to adjust the pH value, natural flocculant algin is added into the waste water to be mixed and held, then the waste water is centrifugally or naturally precipitated and separated to obtain the protein sediment, and finally the protein sediment is dried to obtain the recycled natural and safe protein with strong solubility. By adopting inexpensive and edible raw material algin as the flocculant to process the protein-contained waste water, not only the protein-contained water is adequately purified, but also the recycled protein is free from having any component which is harmful to the human body, and can be widely applicable to the fields such as food, feed and the like. The method also can obtain favorable economic benefit and environmental benefit.
Description
Technical field:
The present invention relates to a kind of albumen recovery method, particularly a kind ofly from contain proteinic wastewater, reclaim proteic method.
Background technology:
In the course of processing of animal/vegetable proteins such as fishery products, meat product, bean product, can produce a large amount of proteinic wastewaters that contains, this type of waste water has organic content height such as albumen, characteristics that chemical oxygen demand is high, if effectively do not handle, serious environment pollution not only, and can waste a large amount of quality protein resources.Adopt suitable method that albumen in the waste water is recycled, not only can avoid the environmental pollution of waste water, and a large amount of protein resource of can regenerating.
Because it is lower to contain the general concentration of proteinic wastewater, if directly carry out concentrate drying, energy consumption is big, and is very uneconomical.Though membrane separation process can reclaim albumen in the waste water, because separatory membrane easily stops up, is difficult to manipulation of regeneration, cost is very high, is difficult to realize the mass-producing application.When the iso-electric point settling process was used separately, effect of settling was undesirable.Flocculence not only can efficient recovery albumen, and simple and easy to do, be easy to mass-producing and use.At present existing multiple flocculation agent is applied to proteic sedimentation and recovery, flocculation agent can be divided into two classes according to the source, one class is the synthetic chemical agent, comprise inorganics and organic polymer materials such as sodium polyacrylate, polyacrylamide such as iron trichloride, Tai-Ace S 150, another kind of is the material of natural origin, comprises mineral material and biomaterials such as tannin, chitosan such as wilkinite, diatomite.Though chemical floc is good to proteic flocculating effect, because it has certain toxic side effect to animal body, so its recovery protein product is difficult to widespread use.Be applied to fields such as feed and food if consider the protein product that will reclaim, then the natural biologic material flocculation agent is best selection.CN 101575371 discloses a kind of method with tannin processing silkworm cocoon processing wastewater and recovery sericin, but because the distinctive astringent taste of tannin, the albumen of recovery is difficult to be widely used in feed and field of food.CN 101624230 discloses a kind of proteic method in the flocculation agent reclaim(ed) sulfuric acid chrondroitin factory effluents such as chitosan of utilizing, the albumen that reclaims can be used as fodder additives and uses, because costing an arm and a leg and often needing of chitosan share with other coagulant aidss, so the economic benefit of this method is not high.
Summary of the invention:
Method based on existing albumen recovery, the object of the invention provides the method that a kind of new processing contains proteinic wastewater, this method can obtain safe and harmless recovery albumen when albumen fully recycles in guaranteeing waste water, can be applicable to fields such as feed and food.
A kind of proteic method that reclaims from contain proteinic wastewater of the present invention is characterized in that: mainly may further comprise the steps:
(1) rough purification is removed and is contained floating in the proteinic wastewater, suspension and impurity such as throw out, pigment;
(2) regulate the pH that contains proteinic wastewater;
(3) add algin, fully stir standing demix;
(4) solid-liquid separation;
(5) drying precipitate.
The described rough purification of step (1) is will contain the floating matter skim in the proteinic wastewater earlier or topple over and remove, then the middle layer is contained proteinic wastewater successively by in stone filtering layer, charcoal filtering layer, sand filter and the gac filtering layer one or more layers, to remove by filter impurity such as suspended substance, pigment, last reject bottom sediment miscellaneous object.Also can will contain after the middle layer sucking-off of proteinic wastewater successively through in stone filtering layer, charcoal filtering layer, sand filter and the gac filtering layer one or more layers and purify by siphonage.
The described adjusting of step (2) contains the pH of proteinic wastewater, looks original the pH difference of waste water, adds an amount of acid or alkali and regulates pH to 3.0-5.5, preferably is adjusted to pH 3.5-5.0.Described acid can be mineral acid, example hydrochloric acid, sulfuric acid, phosphoric acid etc. also can be organic acids, as acetic acid, citric acid, lactic acid etc., can also be above-mentioned multiple mineral acid or organic acid mixing acid, be preferably in the organic acids such as acetic acid, citric acid or lactic acid one or more.Described alkali is the mineral alkali of using always, as sodium hydroxide, potassium hydroxide, ammoniacal liquor etc.
The described algin of step (3) is selected food grade materials for use, and the addition of algin can contain in the proteinic wastewater and to add the 0.1-5.0g algin for every liter, is preferably every liter and contains and add the 1.0-2.0g algin in the proteinic wastewater.Described addition means be with algin earlier with after the abundant heating for dissolving of clear water, pour into again in the waste water, stir then.Described time of repose can be 1-24h, is preferably 8-16h.
The described solid-liquid separation of step (4) can be conventional methods such as centrifugal, heating evaporation, also can adopt siphonage sucking-off supernatant liquor, but should not adopt filtration method.
It is methods such as spraying drying, normal pressure heat drying, vacuum and heating drying or vacuum-freeze-dry that the described drying precipitate of step (5) can adopt.
A kind of proteic method that reclaims from contain proteinic wastewater of the present invention can be applied to proteic recycling in aquatic products processing wastewater (as the rotten poaching wastewater of fish), fowl poultry processing waste water (cutting apart poaching wastewater as the fowl poultry), the bean product processing waste water food industrial wastewaters such as (as bean product compacting waste water).
Technology of the present invention is simple, is easy to realize the mass-producing application.The algin that adopts edible natural to use is that flocculation agent reclaims albumen in the waste water, and any poisonous and harmful element that can not induce one makes the albumen that is reclaimed can be widely used in fields such as feed, food.Used algin is a material cheap and easy to get, and addition is few, and the cost that albumen is reclaimed reduces greatly.Compare with purify the method contain proteinic wastewater with chemical agent, the inventive method has not only realized the purifying treatment of waste water, and reclaims and obtained protein resource, is the method for a kind of environmental benefit and economic benefit bumper harvests.
Embodiment
According to the present invention, a kind ofly from contain proteinic wastewater, reclaim proteic method, can specifically describe by the following examples, but be not limited to the following examples.
Embodiment 1
Floating foam in the rotten poaching wastewater of fish upper strata and impurity are skimmed, with middle layer waste water successively by behind the sand filter, gac filtering layer purifying treatment, HCI with 1.0% and 1.0% NaOH regulate the pH to 4.5 of waste water, take by weighing algin in the ratio of every liter of waste water 1.0g algin, with a small amount of clear water add fully dissolve after, pour in the waste water behind the pH regulator, fully mix, behind the standing demix 8h, centrifugation, be deposited in 50 ℃ of following vacuum-drying 8h, obtain to reclaim albumen.After measured, by recycling, the COD of waste water reduces by 82%, and protein recovery reaches 85%.
Embodiment 2
With the middle layer of the rotten poaching wastewater of fish with the siphonage sucking-off after, successively by after sand filter, the gac filtering layer purifying treatment, the ammoniacal liquor of the citric acid with 1.0% and 1.0% acetic acid and 5.0% is regulated the pH to 5.5 of waste water, takes by weighing algin in the ratio of every liter of waste water 2.0g algin, with a small amount of clear water add fully dissolve after, pour in the waste water behind the pH regulator, fully mix, behind the standing demix 16h, the upper strata stillness of night is removed in siphon, it is spray-dried to precipitate molten slurry, obtains to reclaim albumen.After measured, by recycling, the COD of waste water reduces by 89%, and protein recovery reaches 93%.
Embodiment 3
With the middle layer of the rotten poaching wastewater of fish with the siphonage sucking-off after, after the sand filter purifying treatment, the ammoniacal liquor of the citric acid with 1.0% and 1.0% phosphoric acid and 5.0% is regulated the pH to 5.0 of waste water, takes by weighing algin in the ratio of every liter of waste water 0.5g algin, with a small amount of clear water add fully dissolve after, pour in the waste water behind the pH regulator, fully mix, behind the standing demix 4h, the upper strata stillness of night is removed in siphon, it is spray-dried to precipitate molten slurry, obtains to reclaim albumen.After measured, by recycling, the COD of waste water reduces by 78%, and protein recovery reaches 82%.
Embodiment 4
The upper strata impurity that pork is cut apart poaching wastewater is toppled over and is removed, with the middle layer successively by behind the stone filtering layer, charcoal filtering layer, sand filter, gac filtering layer purifying treatment, citric acid with 1.0% and 5.0% ammoniacal liquor are regulated the pH to 3.5 of waste water, ratio in every liter of waste water 1.5g algin takes by weighing algin, after the abundant dissolving of a small amount of clear water adding, pour in the waste water behind the pH regulator, fully mix, behind the standing demix 10h, the upper strata stillness of night is removed in siphon, it is spray-dried to precipitate molten slurry, obtains to reclaim albumen.After measured, by recycling, the COD of waste water reduces by 86%, and protein recovery reaches 88%.
Embodiment 5
The middle layer of bean product being suppressed waste water with the siphonage sucking-off after layer successively by after charcoal filtering layer, sand filter, the purifying treatment, acetic acid with 1.0% and 1.0% KOH regulate pH to 4.0, ratio in every liter of waste water 5.0g algin takes by weighing algin, after adding fully dissolving with a small amount of clear water, pour in the waste water behind the pH regulator, fully mix, behind the standing demix 24h, centrifugation, precipitation obtain to reclaim albumen through the spray lyophilize.After measured, by recycling, the COD of waste water reduces by 92%, and protein recovery reaches 95%.
Claims (6)
1. one kind is reclaimed proteic method from contain proteinic wastewater, it is characterized in that, mainly may further comprise the steps:
(1) rough purification is removed and is contained floating in the proteinic wastewater, suspension and impurity such as throw out, pigment;
(2) regulate the pH that contains proteinic wastewater;
(3) add algin, fully stir standing demix;
(4) solid-liquid separation;
(5) drying precipitate.
2. a kind of proteic method that from contain proteinic wastewater, reclaims according to claim 1, it is characterized in that: described rough purification is will contain the floating matter skim in the proteinic wastewater earlier or topple over and remove, then with middle layer waste water successively by in stone filtering layer, charcoal filtering layer, sand filter and the gac filtering layer one or more layers, to remove by filter impurity such as suspended substance, pigment, last reject bottom sediment miscellaneous object; Also can will contain after the middle layer sucking-off of proteinic wastewater successively through in stone filtering layer, charcoal filtering layer, sand filter and the gac filtering layer one or more layers and purify by siphonage.
3. a kind of proteic method that from contain proteinic wastewater, reclaims according to claim 1, it is characterized in that: described adjusting contains the pH of proteinic wastewater, look the original pH difference that contains proteinic wastewater, add acid or alkali and be adjusted to pH 3.0-5.5, preferably be adjusted to pH 3.5-5.0.
4. a kind of proteic method that from contain proteinic wastewater, reclaims according to claim 3, it is characterized in that: described acid can be hydrochloric acid, sulfuric acid or the phosphoric acid in the mineral acid, also can be acetic acid, citric acid, the lactic acid in the organic acid, can also be above-mentioned multiple mineral acid or organic acid mixing acid, be preferably in the organic acids such as acetic acid, citric acid or lactic acid one or more.
5. a kind of proteic method that reclaims from contain proteinic wastewater according to claim 3, it is characterized in that: described alkali is sodium hydroxide, potassium hydroxide or the ammoniacal liquor in the mineral alkali of using always.
6. a kind of proteic method that reclaims from contain proteinic wastewater according to claim 1, it is characterized in that: described solid-liquid separation can be the method for the centrifugal or heating evaporation of routine, also can adopt siphonage sucking-off supernatant liquor.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 201010148143 CN101857319A (en) | 2010-04-16 | 2010-04-16 | Method for recycling protein from protein-contained waste water |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 201010148143 CN101857319A (en) | 2010-04-16 | 2010-04-16 | Method for recycling protein from protein-contained waste water |
Publications (1)
Publication Number | Publication Date |
---|---|
CN101857319A true CN101857319A (en) | 2010-10-13 |
Family
ID=42943519
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN 201010148143 Pending CN101857319A (en) | 2010-04-16 | 2010-04-16 | Method for recycling protein from protein-contained waste water |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN101857319A (en) |
Cited By (14)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102774936A (en) * | 2012-05-10 | 2012-11-14 | 江南大学 | Sewage enzyme extraction facility |
CN102849865A (en) * | 2012-09-19 | 2013-01-02 | 宋志娟 | Method for cyclic utilization of soybean product processing waste water and energy-saving apparatus |
CN103214122A (en) * | 2013-05-11 | 2013-07-24 | 桂林理工大学 | Method for treating collagen casing wastewater |
CN103435679A (en) * | 2013-09-03 | 2013-12-11 | 江南大学 | Method for recycling protein from fish soluble |
CN103570177A (en) * | 2013-11-08 | 2014-02-12 | 上海市食品研究所 | Purification treatment process for saliferous pickling wastewater in food industry |
CN104799086A (en) * | 2015-04-24 | 2015-07-29 | 郭忠霖 | Marine product feed and processing technology thereof |
CN104938771A (en) * | 2015-05-29 | 2015-09-30 | 石家庄新宇三阳实业有限公司 | Method for preparing DDG protein feed by protein-containing waste water |
CN107824049A (en) * | 2017-11-13 | 2018-03-23 | 安徽名创新材料科技有限公司 | A kind of method of shearing technique strengthening the membrane separation process |
CN108728287A (en) * | 2017-04-15 | 2018-11-02 | 西南技术物理研究所 | The method for recycling the waste and old laser cleaning liquid of laser water tank |
CN109626636A (en) * | 2018-12-24 | 2019-04-16 | 东莞市健源泉水处理科技有限公司 | A kind of extracting protein from waster water of starch and purification process |
KR102317445B1 (en) * | 2021-03-03 | 2021-10-27 | (주)우리비앤비 | Bio-recovery method of proteins from hydrolysate waste liquid on Crude Heparin Sodium extraction process |
CN113817020A (en) * | 2021-10-18 | 2021-12-21 | 浙江海洋大学 | Method for preparing protein from boiled red shrimp wastewater |
CN115554978A (en) * | 2022-09-26 | 2023-01-03 | 武汉新华扬生物股份有限公司 | Compound for post-treatment of fermentation liquor and post-treatment method of fermentation liquor |
KR20230056506A (en) * | 2021-10-20 | 2023-04-27 | (주)우리비앤비 | Process of recovering heparinoid from alcohol waste water occurring in heparin sodium extracting |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1217890A (en) * | 1997-11-26 | 1999-06-02 | 中国科学院新疆化学研究所 | Method for recovering protein from waste water in production of starch from potatoes |
CN101575371A (en) * | 2009-05-13 | 2009-11-11 | 桂林奥尼斯特节能环保科技有限责任公司 | Method adopting tannin to process silkworm cocoon processing wastewater and recycle sericin protein |
-
2010
- 2010-04-16 CN CN 201010148143 patent/CN101857319A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1217890A (en) * | 1997-11-26 | 1999-06-02 | 中国科学院新疆化学研究所 | Method for recovering protein from waste water in production of starch from potatoes |
CN101575371A (en) * | 2009-05-13 | 2009-11-11 | 桂林奥尼斯特节能环保科技有限责任公司 | Method adopting tannin to process silkworm cocoon processing wastewater and recycle sericin protein |
Non-Patent Citations (2)
Title |
---|
《上海水产大学学报》 19990331 张宗恩等 "鱼糜漂洗液中水溶性蛋白质的回收与利用" 59-62 1-6 第8卷, 第1期 2 * |
《水产科学》 19911231 刘庆慧等 PH对用褐藻胶回收蛋白质的影响 42-43 1-6 第10卷, 第3期 2 * |
Cited By (18)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102774936A (en) * | 2012-05-10 | 2012-11-14 | 江南大学 | Sewage enzyme extraction facility |
CN102849865A (en) * | 2012-09-19 | 2013-01-02 | 宋志娟 | Method for cyclic utilization of soybean product processing waste water and energy-saving apparatus |
CN102849865B (en) * | 2012-09-19 | 2014-02-12 | 宋志娟 | Method for cyclic utilization of soybean product processing waste water and energy-saving apparatus |
CN103214122A (en) * | 2013-05-11 | 2013-07-24 | 桂林理工大学 | Method for treating collagen casing wastewater |
CN103214122B (en) * | 2013-05-11 | 2014-07-30 | 桂林理工大学 | Method for treating collagen casing wastewater |
CN103435679A (en) * | 2013-09-03 | 2013-12-11 | 江南大学 | Method for recycling protein from fish soluble |
CN103570177A (en) * | 2013-11-08 | 2014-02-12 | 上海市食品研究所 | Purification treatment process for saliferous pickling wastewater in food industry |
CN103570177B (en) * | 2013-11-08 | 2014-12-03 | 上海市食品研究所 | Purification treatment process for saliferous pickling wastewater in food industry |
CN104799086A (en) * | 2015-04-24 | 2015-07-29 | 郭忠霖 | Marine product feed and processing technology thereof |
CN104938771A (en) * | 2015-05-29 | 2015-09-30 | 石家庄新宇三阳实业有限公司 | Method for preparing DDG protein feed by protein-containing waste water |
CN108728287A (en) * | 2017-04-15 | 2018-11-02 | 西南技术物理研究所 | The method for recycling the waste and old laser cleaning liquid of laser water tank |
CN107824049A (en) * | 2017-11-13 | 2018-03-23 | 安徽名创新材料科技有限公司 | A kind of method of shearing technique strengthening the membrane separation process |
CN109626636A (en) * | 2018-12-24 | 2019-04-16 | 东莞市健源泉水处理科技有限公司 | A kind of extracting protein from waster water of starch and purification process |
KR102317445B1 (en) * | 2021-03-03 | 2021-10-27 | (주)우리비앤비 | Bio-recovery method of proteins from hydrolysate waste liquid on Crude Heparin Sodium extraction process |
CN113817020A (en) * | 2021-10-18 | 2021-12-21 | 浙江海洋大学 | Method for preparing protein from boiled red shrimp wastewater |
KR20230056506A (en) * | 2021-10-20 | 2023-04-27 | (주)우리비앤비 | Process of recovering heparinoid from alcohol waste water occurring in heparin sodium extracting |
KR102685390B1 (en) | 2021-10-20 | 2024-07-16 | (주)우리비앤비 | Process of recovering heparinoid from alcohol waste water occurring in heparin sodium extracting |
CN115554978A (en) * | 2022-09-26 | 2023-01-03 | 武汉新华扬生物股份有限公司 | Compound for post-treatment of fermentation liquor and post-treatment method of fermentation liquor |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN101857319A (en) | Method for recycling protein from protein-contained waste water | |
Mokhtar et al. | Study on the effectiveness of banana peel coagulant in turbidity reduction of synthetic wastewater | |
CN101624230B (en) | Method of processing waste water and recycling protein | |
CN105439270B (en) | A kind of Moringa oleifera flocculant particle and its production and use | |
Chitra et al. | Performance of natural coagulants on greywater treatment | |
CN105451570B (en) | Method for recovering protein from waste water discharged in fish meat processing product production process | |
Buelna et al. | Evaluation of various flocculants for the recovery of algal biomass grown on pig-waste | |
WO2011119043A1 (en) | Method for removal of contaminations from water | |
Prihatinningtyas | Removal of turbidity in water treatment using natural coagulant from Lemna perpusilla | |
CN106396168B (en) | Marble effluent disposal system | |
CN103864911B (en) | A kind of composite flocculation agent is used to reclaim the method for water soluble protein in minced fillet washings | |
US4869829A (en) | Process for separating solids with a keratin filter aid | |
CN109370446B (en) | Method for clarifying gelatin solution by comprehensively utilizing waste residues | |
CA2796713A1 (en) | Method for treating water by ballasted flocculation implementing a natural flocculent | |
Johnson et al. | Use of coagulants to treat seafood processing wastewaters | |
KR100926382B1 (en) | Method of producing filter material comprising bottom ash | |
US20200236964A1 (en) | Method for collecting proteins from washwater and/or wastewater | |
EP3585757A1 (en) | A process for forming a product solution from poultry waste digestate | |
CN211004941U (en) | Water circulation treatment system for farm | |
Pambi et al. | Influence of Effluent Type on the Performance of Chitosan as a Coagulant | |
CN114906963A (en) | Comprehensive utilization process of animal viscera extraction wastewater | |
CN104938771A (en) | Method for preparing DDG protein feed by protein-containing waste water | |
KR101214371B1 (en) | Treatment method of wastewater containing strong nitrogenous | |
CN106335989B (en) | A kind of preparation method of sanitary sewage detergent | |
JPH0553521B2 (en) |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C02 | Deemed withdrawal of patent application after publication (patent law 2001) | ||
WD01 | Invention patent application deemed withdrawn after publication |
Open date: 20101013 |