CN108083434A - A kind of method for handling kitchen waste water - Google Patents
A kind of method for handling kitchen waste water Download PDFInfo
- Publication number
- CN108083434A CN108083434A CN201810062686.5A CN201810062686A CN108083434A CN 108083434 A CN108083434 A CN 108083434A CN 201810062686 A CN201810062686 A CN 201810062686A CN 108083434 A CN108083434 A CN 108083434A
- Authority
- CN
- China
- Prior art keywords
- waste water
- column
- anaerobism
- kitchen waste
- ethyl alcohol
- 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.)
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Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/28—Anaerobic digestion processes
- C02F3/2813—Anaerobic digestion processes using anaerobic contact processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological 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
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/28—Anaerobic digestion processes
- C02F3/2806—Anaerobic processes using solid supports for microorganisms
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/28—Anaerobic digestion processes
- C02F3/286—Anaerobic digestion processes including two or more steps
Abstract
The present invention provides a kind of methods for handling kitchen waste water.Comprise the following steps：(1) anaerobism section sludge is taken to be packed into after being mixed with kitchen waste water in anaerobism column, is precipitated after stirring, discharges base sludge；(2) biofilm packing is added in anaerobism column, starts the continuum micromeehanics in anaerobism column, reacted after water in column is full, wherein, the biofilm packing is prepared by following component：The first step：By lac resin and absolute ethyl alcohol mixed dissolution；Second step：Add in anionic cellulose, sepiolite clay and peanut hull biologic charcoal ball milling；3rd step：Add in residual components, microwave treatment, supersonic oscillations；4th step：After absolute ethyl alcohol volatilization to the greatest extent, it is put into double screw extruder extruding pelletization to obtain the final product；(3) water handled well is discharged, measures its index.The object of the present invention is to provide a kind of methods for handling kitchen waste water, can remove effectively the grease in waste water, all fine simultaneously for the removal effect of COD in waste water and BOD.
Description
Technical field
The present invention relates to a kind of methods for handling kitchen waste water.
Background technology
With the rapid economic development in our country, catering trade, tourist industry also grow up therewith, the relevant issues brought are exactly
Come from the pollution of kitchen waste water in the catering trades such as each hotel, the wastewater flow rate of discharge is increasing, makes food and drink waste water
Pollution becoming serious.Due to the vegetable and animals oils containing higher concentration and a large amount of solid suspensions in the waste water, so making
It becomes an important pollution entering the water.Food and drink waste water has the characteristics of BOD, COD concentration are high, and oil content is more, and discharge capacity is big, together
When due in this kind of waste water noxious material it is relatively fewer, the general unprocessed rich battalion for being just directly discharged to water body, causing water body
Fosterization is oil removing for the main problem in sewage from catering business processing, reduces CODCr and turbidity.The processing of kitchen waste water can not only
It preserves the ecological environment, and the burden at municipal sewage treatment station can be mitigated, there is apparent environmental benefit and economic benefit.
The content of the invention
Technical problems to be solved：The object of the present invention is to provide a kind of methods for handling kitchen waste water, can be effectively
The grease in waste water is removed, it is all fine simultaneously for the removal effect of COD in waste water and BOD.
Technical solution：A kind of method for handling kitchen waste water, comprises the following steps：
(1) anaerobism section sludge is taken to be packed into after being mixed with kitchen waste water in anaerobism column, 2~3h, discharge are precipitated after continuously stirring 5~6h
Base sludge；
(2) biofilm packing is added in anaerobism column, starts the continuum micromeehanics in anaerobism column, after water in column is full, reaction 6~
7h；
(3) water handled well is discharged, measures its index.
Further, the biofilm packing is prepared by following component：50~55g of polystyrene adsorption resin, shellac tree
3~5g of fat, 10~18g of sulfydryl silica gel, 3~7g of anionic cellulose, 2~5g of sepiolite clay, peanut hull biologic charcoal 10~
20g, 2~5g of straw alkali lignin, 1~3g of Soy 11 S Globulin, 0.5~1g of cerous sulfate, 20~30g of absolute ethyl alcohol, preparation side
Method is：
The first step：By lac resin and absolute ethyl alcohol mixed dissolution；
Second step：Add in anionic cellulose, sepiolite clay and peanut hull biologic charcoal, be put into ball milling 2 in planetary ball mill~
4h；
3rd step：Add in residual components, 3~4min of microwave treatment, supersonic oscillations 1h under 750~800W of power；
4th step：After absolute ethyl alcohol volatilization to the greatest extent, it is put into double screw extruder to carry out squeezing out at 240~250 DEG C of temperature and makes
Grain to obtain the final product.
Further, biofilm packing accounts for the 10% of anaerobism column volume in the step (2).
Further, extrusion temperature is 245 DEG C in the 4th step in the preparation method of the biofilm packing.
Advantageous effect：This method can remove effectively the grease in waste water, and the removal simultaneously for COD in waste water and BOD is imitated
Fruit is all fine, and highest removal rate respectively reaches 96.2% and 94.3%.
Specific embodiment
Embodiment 1
A kind of method for handling kitchen waste water, comprises the following steps：
(1) anaerobism section sludge is taken to be packed into after being mixed with kitchen waste water in anaerobism column, precipitates 2h after continuously stirring 5h, discharge bottom is dirty
Mud；
(2) biofilm packing is added in anaerobism column, starts the continuum micromeehanics in anaerobism column, after water in column is full, react 6h,
In, the biofilm packing is prepared by following component：Polystyrene adsorption resin 50g, lac resin 3g, sulfydryl silica gel
10g, anionic cellulose 3g, sepiolite clay 2g, peanut hull biologic charcoal 10g, straw alkali lignin 2g, Soy 11 S Globulin
1g, cerous sulfate 0.5g, absolute ethyl alcohol 20g, preparation method are：
The first step：By lac resin and absolute ethyl alcohol mixed dissolution；
Second step：Anionic cellulose, sepiolite clay and peanut hull biologic charcoal are added in, is put into ball milling 2h in planetary ball mill；
3rd step：Add in residual components, microwave treatment 3min, supersonic oscillations 1h under power 750W；
4th step：After absolute ethyl alcohol volatilization to the greatest extent, it is put into double screw extruder and carries out extruding pelletization i.e. at 240 DEG C of temperature
；
(3) water handled well is discharged, measures its index.
Embodiment 2
A kind of method for handling kitchen waste water, comprises the following steps：
(1) anaerobism section sludge is taken to be packed into after being mixed with kitchen waste water in anaerobism column, 2.5h is precipitated after continuously stirring 5.5h, discharges bottom
Portion's sludge；
(2) biofilm packing is added in anaerobism column, starts the continuum micromeehanics in anaerobism column, after water in column is full, react 6.5h,
Wherein, the biofilm packing is prepared by following component：Polystyrene adsorption resin 52g, lac resin 4g, sulfydryl silica gel
14g, anionic cellulose 5g, sepiolite clay 3g, peanut hull biologic charcoal 15g, straw alkali lignin 3g, Soy 11 S Globulin
2g, cerous sulfate 0.7g, absolute ethyl alcohol 25g, preparation method are：
The first step：By lac resin and absolute ethyl alcohol mixed dissolution；
Second step：Anionic cellulose, sepiolite clay and peanut hull biologic charcoal are added in, is put into ball milling 3h in planetary ball mill；
3rd step：Add in residual components, microwave treatment 3min, supersonic oscillations 1h under power 780W；
4th step：After absolute ethyl alcohol volatilization to the greatest extent, it is put into double screw extruder and carries out extruding pelletization i.e. at 245 DEG C of temperature
；
(3) water handled well is discharged, measures its index.
Embodiment 3
A kind of method for handling kitchen waste water, comprises the following steps：
(1) anaerobism section sludge is taken to be packed into after being mixed with kitchen waste water in anaerobism column, precipitates 3h after continuously stirring 6h, discharge bottom is dirty
Mud；
(2) biofilm packing is added in anaerobism column, starts the continuum micromeehanics in anaerobism column, after water in column is full, react 7h,
In, the biofilm packing is prepared by following component：Polystyrene adsorption resin 55g, lac resin 5g, sulfydryl silica gel
18g, anionic cellulose 7g, sepiolite clay 5g, peanut hull biologic charcoal 20g, straw alkali lignin 5g, Soy 11 S Globulin
3g, cerous sulfate 1g, absolute ethyl alcohol 30g, preparation method are：
The first step：By lac resin and absolute ethyl alcohol mixed dissolution；
Second step：Anionic cellulose, sepiolite clay and peanut hull biologic charcoal are added in, is put into ball milling 4h in planetary ball mill；
3rd step：Add in residual components, microwave treatment 4min, supersonic oscillations 1h under power 800W；
4th step：After absolute ethyl alcohol volatilization to the greatest extent, it is put into double screw extruder and carries out extruding pelletization i.e. at 250 DEG C of temperature
；
(3) water handled well is discharged, measures its index.
Comparative example 1
A kind of method for handling kitchen waste water, comprises the following steps：
(1) biofilm packing is added in anaerobism column, starts the continuum micromeehanics in anaerobism column, after water in column is full, react 6h,
In, the biofilm packing is prepared by following component：Polystyrene adsorption resin 50g, lac resin 3g, sulfydryl silica gel
10g, anionic cellulose 3g, sepiolite clay 2g, peanut hull biologic charcoal 11g, straw alkali lignin 2g, Soy 11 S Globulin
1g, cerous sulfate 0.5g, absolute ethyl alcohol 20g, preparation method are：
The first step：By lac resin and absolute ethyl alcohol mixed dissolution；
Second step：Anionic cellulose, sepiolite clay and peanut hull biologic charcoal are added in, is put into ball milling 2h in planetary ball mill；
3rd step：Add in residual components, microwave treatment 3min, supersonic oscillations 1h under power 750W；
4th step：After absolute ethyl alcohol volatilization to the greatest extent, it is put into double screw extruder and carries out extruding pelletization i.e. at 230 DEG C of temperature
；
(2) water handled well is discharged, measures its index.
Comparative example 2
A kind of method for handling kitchen waste water, comprises the following steps：
(1) anaerobism section sludge is taken to be packed into after being mixed with kitchen waste water in anaerobism column, precipitates 2h after continuously stirring 5h, discharge bottom is dirty
Mud；
(2) start the continuum micromeehanics in anaerobism column, after water in column is full, react 6h；
(3) water handled well is discharged, measures its index.
Table 1
| Name of product | Oil content (mg/L) | COD removal rates (%) | BOD removal rates (%) |
| Embodiment 1 | 9.64 | 95.7 | 94.1 |
| Embodiment 2 | 9.36 | 95.9 | 94.2 |
| Embodiment 3 | 9.19 | 96.2 | 94.3 |
| Comparative example 1 | 18.35 | 85.3 | 81.9 |
| Comparative example 2 | 29.78 | 9.4 | 0.6 |
Note：Oil content is 69.3mg/L in raw wastewater, and COD concentration and BOD concentration are respectively 1212.32mg/L, 1024.68mg/L
The partial properties index of water is seen the above table after the method for the present invention processing, it will be seen that this method can remove effectively
Grease in waste water, all fine simultaneously for the removal effect of COD in waste water and BOD, highest removal rate respectively reaches
96.2% and 94.3%.
Claims (4)
- A kind of 1. method for handling kitchen waste water, it is characterised in that：Comprise the following steps：(1) anaerobism section sludge is taken to be packed into after being mixed with kitchen waste water in anaerobism column, 2~3h, discharge are precipitated after continuously stirring 5~6h Base sludge；(2) biofilm packing is added in anaerobism column, starts the continuum micromeehanics in anaerobism column, after water in column is full, reaction 6~ 7h；(3) water handled well is discharged, measures its index.
- 2. a kind of method for handling kitchen waste water as described in claim 1, it is characterised in that：The biofilm packing is by following Ingredient is prepared：50~55g of polystyrene adsorption resin, 3~5g of lac resin, 10~18g of sulfydryl silica gel, anion fiber 3~7g of element, 2~5g of sepiolite clay, 10~20g of peanut hull biologic charcoal, 2~5g of straw alkali lignin, Soy 11 S Globulin 1 ~3g, 0.5~1g of cerous sulfate, 20~30g of absolute ethyl alcohol, preparation method are：The first step：By lac resin and absolute ethyl alcohol mixed dissolution；Second step：Add in anionic cellulose, sepiolite clay and peanut hull biologic charcoal, be put into ball milling 2 in planetary ball mill~ 4h；3rd step：Add in residual components, 3~4min of microwave treatment, supersonic oscillations 1h under 750~800W of power；4th step：After absolute ethyl alcohol volatilization to the greatest extent, it is put into double screw extruder to carry out squeezing out at 240~250 DEG C of temperature and makes Grain to obtain the final product.
- 3. a kind of method for handling kitchen waste water according to claim 1, it is characterised in that：It is biological in the step (2) Film filler accounts for the 10% of anaerobism column volume.
- 4. a kind of method for handling kitchen waste water according to claim 2, it is characterised in that：The biofilm packing Extrusion temperature is 245 DEG C in the 4th step in preparation method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810062686.5A CN108083434B (en) | 2018-01-22 | 2018-01-22 | Method for treating kitchen wastewater |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810062686.5A CN108083434B (en) | 2018-01-22 | 2018-01-22 | Method for treating kitchen wastewater |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN108083434A true CN108083434A (en) | 2018-05-29 |
| CN108083434B CN108083434B (en) | 2021-08-24 |
Family
ID=62182514
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201810062686.5A Active CN108083434B (en) | 2018-01-22 | 2018-01-22 | Method for treating kitchen wastewater |
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|---|---|
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Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109502734A (en) * | 2019-01-07 | 2019-03-22 | 李豪 | A kind of use in waste water treatment biofilm packing and the method with its processing waste water |
| CN113233582A (en) * | 2021-06-25 | 2021-08-10 | 重庆普康生物科技有限公司 | Ecological water treatment process |
Citations (19)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002219482A (en) * | 2001-01-24 | 2002-08-06 | Mitsubishi Kakoki Kaisha Ltd | Wastewater treatment equipment |
| CN2622167Y (en) * | 2003-02-24 | 2004-06-30 | 上海理工大学 | Batch-type activated sludge method equipment for treating kitchen waste-water |
| CN200967775Y (en) * | 2006-10-09 | 2007-10-31 | 南京师范大学 | Composite UBF anaerobic organism waste water treatment reactor |
| CN101580333A (en) * | 2009-06-29 | 2009-11-18 | 杭州富春环保工程有限公司 | Domestic sewage disposal device and treatment method thereof |
| CN201737770U (en) * | 2010-03-22 | 2011-02-09 | 南京加德绿色能源研发有限公司 | Microbial response system for waste water treatment and clean energy production at the same time |
| CN102583736A (en) * | 2012-01-30 | 2012-07-18 | 湖北君集水处理有限公司 | Sewage biochemical treatment process and device utilizing active sludge and biological membrane combined circulating flow |
| CN103508623A (en) * | 2012-06-29 | 2014-01-15 | 中国海洋石油总公司 | Treatment method of coal gasification wastewater |
| CN203474603U (en) * | 2013-09-25 | 2014-03-12 | 武汉市润绿环保科技有限公司 | Sewage continuous flow A2O biochemical reaction and sludge static precipitation integrated device |
| CN103723893A (en) * | 2014-01-10 | 2014-04-16 | 中国科学院生态环境研究中心 | Method for removing nitrate nitrogen from water |
| CN104773822A (en) * | 2015-04-21 | 2015-07-15 | 牧原食品股份有限公司 | Anaerobic tank liquid high-efficiency return method and device |
| CN104944706A (en) * | 2015-06-24 | 2015-09-30 | 安徽显闰环境工程有限公司 | Sewage treatment device |
| CN106006947A (en) * | 2016-05-26 | 2016-10-12 | 南京国龙生物科技有限公司 | Biological membrane packing for treating livestock and poultry breeding wastewater and preparation technology of biological membrane packing |
| CN106336000A (en) * | 2016-08-29 | 2017-01-18 | 浙江恒生印染有限公司 | Phosphorus-free environment-friendly sewage treatment method |
| CN106430569A (en) * | 2016-11-22 | 2017-02-22 | 中国华电科工集团有限公司 | Kitchen waste wastewater treatment method and device |
| CN106745724A (en) * | 2017-02-10 | 2017-05-31 | 苏州苏科环保科技有限公司 | A kind of kitchen waste water anaerobism MBR processing equipments |
| CN206289048U (en) * | 2016-11-25 | 2017-06-30 | 湖北水云涧环保工程有限公司 | Sewage combination biochemistry and sludge static state deposition separating treatment integrated apparatus |
| CN107082488A (en) * | 2017-02-23 | 2017-08-22 | 苏州康顿环保科技有限公司 | The anaerobic membrane bioreactor and its processing method of a kind of effective processing kitchen waste water |
| CN107162198A (en) * | 2017-07-20 | 2017-09-15 | 重庆阳正环保科技股份有限公司 | A kind of highly difficult waste water purification device |
| CN108217939A (en) * | 2017-12-18 | 2018-06-29 | 桑德生态科技有限公司 | Anaerobic-aerobic moving-bed biofilm reaction system handles the startup method of high ammonia-nitrogen wastewater |
-
2018
- 2018-01-22 CN CN201810062686.5A patent/CN108083434B/en active Active
Patent Citations (19)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002219482A (en) * | 2001-01-24 | 2002-08-06 | Mitsubishi Kakoki Kaisha Ltd | Wastewater treatment equipment |
| CN2622167Y (en) * | 2003-02-24 | 2004-06-30 | 上海理工大学 | Batch-type activated sludge method equipment for treating kitchen waste-water |
| CN200967775Y (en) * | 2006-10-09 | 2007-10-31 | 南京师范大学 | Composite UBF anaerobic organism waste water treatment reactor |
| CN101580333A (en) * | 2009-06-29 | 2009-11-18 | 杭州富春环保工程有限公司 | Domestic sewage disposal device and treatment method thereof |
| CN201737770U (en) * | 2010-03-22 | 2011-02-09 | 南京加德绿色能源研发有限公司 | Microbial response system for waste water treatment and clean energy production at the same time |
| CN102583736A (en) * | 2012-01-30 | 2012-07-18 | 湖北君集水处理有限公司 | Sewage biochemical treatment process and device utilizing active sludge and biological membrane combined circulating flow |
| CN103508623A (en) * | 2012-06-29 | 2014-01-15 | 中国海洋石油总公司 | Treatment method of coal gasification wastewater |
| CN203474603U (en) * | 2013-09-25 | 2014-03-12 | 武汉市润绿环保科技有限公司 | Sewage continuous flow A2O biochemical reaction and sludge static precipitation integrated device |
| CN103723893A (en) * | 2014-01-10 | 2014-04-16 | 中国科学院生态环境研究中心 | Method for removing nitrate nitrogen from water |
| CN104773822A (en) * | 2015-04-21 | 2015-07-15 | 牧原食品股份有限公司 | Anaerobic tank liquid high-efficiency return method and device |
| CN104944706A (en) * | 2015-06-24 | 2015-09-30 | 安徽显闰环境工程有限公司 | Sewage treatment device |
| CN106006947A (en) * | 2016-05-26 | 2016-10-12 | 南京国龙生物科技有限公司 | Biological membrane packing for treating livestock and poultry breeding wastewater and preparation technology of biological membrane packing |
| CN106336000A (en) * | 2016-08-29 | 2017-01-18 | 浙江恒生印染有限公司 | Phosphorus-free environment-friendly sewage treatment method |
| CN106430569A (en) * | 2016-11-22 | 2017-02-22 | 中国华电科工集团有限公司 | Kitchen waste wastewater treatment method and device |
| CN206289048U (en) * | 2016-11-25 | 2017-06-30 | 湖北水云涧环保工程有限公司 | Sewage combination biochemistry and sludge static state deposition separating treatment integrated apparatus |
| CN106745724A (en) * | 2017-02-10 | 2017-05-31 | 苏州苏科环保科技有限公司 | A kind of kitchen waste water anaerobism MBR processing equipments |
| CN107082488A (en) * | 2017-02-23 | 2017-08-22 | 苏州康顿环保科技有限公司 | The anaerobic membrane bioreactor and its processing method of a kind of effective processing kitchen waste water |
| CN107162198A (en) * | 2017-07-20 | 2017-09-15 | 重庆阳正环保科技股份有限公司 | A kind of highly difficult waste water purification device |
| CN108217939A (en) * | 2017-12-18 | 2018-06-29 | 桑德生态科技有限公司 | Anaerobic-aerobic moving-bed biofilm reaction system handles the startup method of high ammonia-nitrogen wastewater |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109502734A (en) * | 2019-01-07 | 2019-03-22 | 李豪 | A kind of use in waste water treatment biofilm packing and the method with its processing waste water |
| CN113233582A (en) * | 2021-06-25 | 2021-08-10 | 重庆普康生物科技有限公司 | Ecological water treatment process |
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| Publication number | Publication date |
|---|---|
| CN108083434B (en) | 2021-08-24 |
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