JP2003285099A - Treatment method for brewing waste liquid - Google Patents

Treatment method for brewing waste liquid

Info

Publication number
JP2003285099A
JP2003285099A JP2002087900A JP2002087900A JP2003285099A JP 2003285099 A JP2003285099 A JP 2003285099A JP 2002087900 A JP2002087900 A JP 2002087900A JP 2002087900 A JP2002087900 A JP 2002087900A JP 2003285099 A JP2003285099 A JP 2003285099A
Authority
JP
Japan
Prior art keywords
waste liquid
liquid
solution
treatment
treating
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
Application number
JP2002087900A
Other languages
Japanese (ja)
Inventor
Takashi Sasahira
俊 笹平
Masashi Kaneko
政司 金子
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.)
NTT Auto Leasing Co Ltd
Original Assignee
NTT Auto Leasing Co Ltd
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 NTT Auto Leasing Co Ltd filed Critical NTT Auto Leasing Co Ltd
Priority to JP2002087900A priority Critical patent/JP2003285099A/en
Publication of JP2003285099A publication Critical patent/JP2003285099A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Separation Using Semi-Permeable Membranes (AREA)
  • Activated Sludge Processes (AREA)
  • Treatment Of Sludge (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)
  • Distillation Of Fermentation Liquor, Processing Of Alcohols, Vinegar And Beer (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a treatment method for a brewing waste liquid for treating the brewing waste liquid certainly and efficiently to obtain dischargeable water and separating a reutilizable component contained in the waste liquid efficiently to reutilize the same. <P>SOLUTION: The treatment method for the brewing waste liquid includes a process for subjecting the brewing waste liquid to solid-liquid separation treatment, a process for filtering the solution separated in the solid-liquid separation process, a process for electrodialyzing the filtered solution to separate an ion component and a process for treating the solution, from which the ion component is separated, with activated sludge. <P>COPYRIGHT: (C)2004,JPO

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、醸造廃液の処理方
法に関し、とくに、焼酎製造工程からの廃液の処理等に
好適な醸造廃液の処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating brewing waste liquor, and more particularly to a method for treating brewing waste liquor suitable for treating waste liquor from a shochu manufacturing process.

【0002】[0002]

【従来の技術】大量に排出される醸造廃液、たとえば焼
酎製造工程から排出される廃液には、固相成分が含まれ
ているとともに、アミノ酸や、酢酸やクエン酸等の有機
酸がイオン成分として高濃度(1〜2%程度)に含まれ
ている。従来、このような醸造廃液を大量に処理する方
法として、有効な、あるいは精度のよい処理方法は未だ
開発されておらず、高々、醸造廃液を固液分離して、分
離された固相や液相をそのまま保管する方法、液相を活
性汚泥処理に供する方法などが採用されている。
2. Description of the Related Art A large amount of brewing waste liquor, for example, the liquor discharged from the shochu manufacturing process, contains a solid phase component and also contains amino acids and organic acids such as acetic acid and citric acid as ionic components. It is contained in a high concentration (about 1 to 2%). Conventionally, as a method for treating a large amount of such brewing waste liquid, an effective or accurate treatment method has not yet been developed, and at most, the brewing waste liquid is solid-liquid separated to separate the separated solid phase or liquid. A method of storing the phase as it is, a method of subjecting the liquid phase to activated sludge treatment, and the like are adopted.

【0003】しかし、単に保管するだけでは、廃液が大
量に排出されてくることから、直ぐに保管場所に行き詰
まりが生じる。また、固液分離処理を施すだけでは、そ
の液相成分は未だ大量のコロイドや多糖類、タンパク質
等を含んでいるとともに、上述の如く高濃度でアミノ酸
や有機酸をイオン成分として含んでいるので、そのまま
放流するには問題がある。したがって、活性汚泥処理等
に供することになるが、直に活性汚泥処理に供しても、
上記のような分離すべき成分を十分に分離除去すること
は難しく、また、活性汚泥処理設備として、著しく大型
の設備が必要となる。さらに、活性汚泥処理後の処理水
を放流するには、そのBODを十分に低い値にまで下げ
る必要があるが、上記のような簡単な工程の組み合わせ
のみでは、BODを十分に下げることは難しい。したが
って、放流するための水質を十分に確保できていないの
が実情である。
However, if it is simply stored, a large amount of waste liquid will be discharged, so that the storage location will soon get stuck. In addition, since only the solid-liquid separation treatment is performed, the liquid phase component still contains a large amount of colloids, polysaccharides, proteins and the like, and as described above, it contains amino acids and organic acids at high concentrations as ionic components. , There is a problem to release it as it is. Therefore, although it will be subjected to activated sludge treatment, etc., even if it is directly subjected to activated sludge treatment,
It is difficult to sufficiently separate and remove the components to be separated as described above, and a remarkably large-sized facility is required as the activated sludge treatment facility. Furthermore, in order to discharge the treated water after the activated sludge treatment, it is necessary to lower the BOD to a sufficiently low value, but it is difficult to lower the BOD sufficiently only by combining the above-mentioned simple steps. . Therefore, the reality is that the water quality for discharge is not sufficiently secured.

【0004】[0004]

【発明が解決しようとする課題】そこで本発明の課題
は、上記のような実情に鑑み、醸造廃液を放流できる水
質まで確実にかつ効率よく処理するとともに、廃液中に
含まれていた再利用可能な成分を効率よく分離し再利用
に供することを可能とする、醸造廃液の処理方法を提供
することにある。
Therefore, in view of the above-mentioned circumstances, an object of the present invention is to reliably and efficiently treat even the quality of water capable of discharging brewing waste liquid, and to reuse the waste water contained in the waste liquid. Another object of the present invention is to provide a method for treating waste brewing liquid, which enables efficient separation of various components and reuse.

【0005】[0005]

【課題を解決するための手段】上記課題を解決するため
に、本発明に係る醸造廃液の処理方法は、醸造廃液を固
液分離する工程、該固液分離工程により分離された溶液
を濾過する工程、濾過後の溶液を電気透析しイオン成分
を分離する工程、イオン成分が分離された溶液を活性汚
泥処理する工程を含むことを特徴とする方法からなる。
In order to solve the above problems, a method for treating a brewing waste liquid according to the present invention comprises a step of solid-liquid separating the brewing waste liquid, and a solution separated by the solid-liquid separation step. The method comprises a step, a step of electrodialyzing the solution after filtration to separate an ionic component, and a step of treating the solution from which the ionic component has been separated with activated sludge.

【0006】この醸造廃液の処理方法は、さらに、上記
固液分離工程により分離された固相成分を水分調整した
後(たとえば、水分調整剤を添加した後)、該固相成分
に上記電気透析工程により分離されたイオン成分を混合
する工程を有していてもよい。さらにまた、このイオン
成分と固相成分との混合物を乾燥する工程を有していて
もよい。乾燥には、スプレードライ処理などを適用すれ
ばよい。乾燥された混合物は、アミノ酸等の成分が濃縮
された形で含まれているので、たとえば家畜用等の飼料
の原料として再利用することが可能になる。
This method for treating waste brewing liquid further comprises adjusting the water content of the solid phase component separated in the solid-liquid separation step (for example, after adding a water content adjusting agent), and then performing the electrodialysis on the solid phase component. You may have the process of mixing the ionic component isolate | separated by the process. Further, it may have a step of drying the mixture of the ionic component and the solid phase component. For drying, spray drying treatment or the like may be applied. Since the dried mixture contains the components such as amino acids in a concentrated form, it can be reused as a raw material of feed for livestock, for example.

【0007】また、上記醸造廃液の処理方法は、さら
に、上記電気透析工程によるイオン成分が分離された溶
液を、活性汚泥処理するに際し希釈する工程を有してい
てもよい。希釈により、活性汚泥処理前に被処理水のB
OD値を適切に低下させることができ、より効果的に活
性汚泥処理を行うことができる。希釈液としては、その
少なくとも一部に、活性汚泥処理工程からの処理液を使
用することができ、それによって、効率のよい処理シス
テムとなる。このような活性汚泥処理後の処理水は、そ
のBOD値を十分に低い値にまで低下させることが可能
となるので、問題を生じることなく放流することが可能
になる。
Further, the treatment method of the brewing waste liquid may further have a step of diluting the solution from which the ionic components have been separated by the electrodialysis step when the activated sludge is treated. Due to dilution, B of treated water before activated sludge treatment
The OD value can be appropriately reduced, and the activated sludge treatment can be performed more effectively. As the diluting liquid, the treatment liquid from the activated sludge treatment process can be used for at least a part thereof, thereby providing an efficient treatment system. Since the BOD value of the treated water after the activated sludge treatment can be lowered to a sufficiently low value, the treated water can be discharged without causing a problem.

【0008】上記のような本発明に係る醸造廃液の処理
方法においては、醸造工程から排出されてきた醸造廃液
が、そのまま移送ラインにより、あるいは、輸送手段に
よる廃液処理工場への運搬により、固液分離工程に供給
され、固相と液相とに分離される。分離された液相の溶
液は、まず、濾過工程に供給され、濾過により、溶液中
のコロイド成分、多糖類成分、タンパク質成分などの、
固液分離工程では除去し得なかった成分が除去される。
これらの成分が除去された濾過後の溶液は、電気透析工
程に供給され、ここで電気透析により溶液中のイオン成
分が透析分離される。このイオン成分には、アミノ酸
や、酢酸、クエン酸等の有機酸などの再利用可能な成分
が含まれている。イオン成分の分離除去された溶液が、
活性汚泥処理工程に送られ、活性汚泥処理に供せられ
る。
In the method for treating a brewing waste liquid according to the present invention as described above, the brewing waste liquid discharged from the brewing process is directly transferred to the waste liquid treatment factory by a transfer line or is transported to a waste liquid treatment factory by a transportation means to form a solid-liquid solution. It is supplied to the separation step and separated into a solid phase and a liquid phase. The separated liquid phase solution is first supplied to the filtration step, and by filtration, such as the colloidal component, the polysaccharide component and the protein component in the solution,
Components that could not be removed in the solid-liquid separation step are removed.
The filtered solution from which these components have been removed is supplied to the electrodialysis step, where the ionic components in the solution are dialyzed and separated by electrodialysis. This ionic component contains reusable components such as amino acids and organic acids such as acetic acid and citric acid. The solution from which the ionic components have been separated and removed is
It is sent to the activated sludge treatment process and used for activated sludge treatment.

【0009】上記一連の固液分離後の溶液処理において
は、濾過によるコロイド成分等の分離除去により溶液の
BODが低下され、次に電気透析によるイオン成分の分
離除去により溶液のBODがさらに低下され、さらに、
活性汚泥処理によりBODがさらに低下されて、最終的
に、放流可能な十分に低いBOD値の処理水が得られ
る。活性汚泥処理前に希釈すれば、さらに迅速に効率よ
く所望のBOD値の処理水が得られる。そして、BOD
値が十分に低下された活性汚泥処理水は、問題を生じる
ことなく、放流することが可能となる。また、これら一
連の処理は、連続的な処理として行うことが可能である
ので、大量の廃液に対しても、それに見合う設備を設置
して運転することにより、効率のよい連続処理が可能と
なる。
In the solution treatment after the above series of solid-liquid separation, the BOD of the solution is lowered by separating and removing the colloidal components and the like by filtration, and then the BOD of the solution is further lowered by separating and removing the ionic components by electrodialysis. ,further,
The activated sludge treatment further lowers the BOD, and finally, treated water having a sufficiently low BOD value that can be discharged is obtained. If diluted before the activated sludge treatment, treated water having a desired BOD value can be obtained more quickly and efficiently. And BOD
The activated sludge treated water whose value has been sufficiently reduced can be discharged without causing any problems. Further, since this series of treatments can be performed as a continuous treatment, efficient continuous treatment can be performed even for a large amount of waste liquid by installing and operating equipment suitable for it. .

【0010】一方、固液分離後の固相に対しては、その
まま乾燥等の処理に供することも可能であり、あるい
は、水分調整を施した後前記電気透析により分離された
イオン成分を攪拌・混合し、イオン成分の再利用をはか
ることも可能である。イオン成分の再利用に際しては、
利用しやすい形態とするために、固相とイオン成分との
混合物を乾燥すればよい。とくにアミノ酸等を含有した
乾燥混合物は、家畜などの飼料の原料として再利用可能
なものである。したがって、本発明方法は、廃液中に含
まれていた再利用可能な成分を効率よく分離し再利用に
供することも可能とするものである。
On the other hand, the solid phase after the solid-liquid separation can be directly subjected to a treatment such as drying, or the ionic component separated by the electrodialysis after stirring the water content can be stirred and It is also possible to mix and reuse the ionic components. When reusing the ionic components,
The mixture of the solid phase and the ionic component may be dried to provide a form that is easy to use. Particularly, a dry mixture containing amino acids and the like can be reused as a raw material for feed for livestock. Therefore, the method of the present invention makes it possible to efficiently separate and reuse the reusable components contained in the waste liquid.

【0011】[0011]

【発明の実施の形態】以下に、本発明の望ましい実施の
形態を、図面を参照して説明する。図1は、本発明の一
実施態様に係る醸造廃液の処理方法の工程フローを示し
ている。図1において、1は、焼酎の製造工程等から排
出されてきた醸造廃液を示しており(たとえば、100
tの醸造廃液)、たとえばホットチャージ車2により、
醸造廃液処理工場3に運搬される。運搬の際には、通気
を確保しながら、水分を一部蒸発させるようにすること
もできる。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENT A preferred embodiment of the present invention will be described below with reference to the drawings. FIG. 1 shows a process flow of a method for treating brewery waste liquid according to an embodiment of the present invention. In FIG. 1, reference numeral 1 indicates a brewing waste liquid discharged from the shochu manufacturing process or the like (for example, 100
brewing waste liquid of t), for example, by the hot charge car 2,
Transported to the brewery waste liquid treatment plant 3. During transportation, it is possible to partially evaporate the water while ensuring ventilation.

【0012】醸造廃液処理工場3では、まず、固液分離
装置による固液分離工程4に供給される。固液分離工程
4では、固相5(たとえば、10t)と液相6(たとえ
ば、90t)とに分離される。分離された液相6の溶液
は、焼酎製造工程からの醸造廃液の場合、通常、80,
000ppm程度のBOD値を示す。
In the brewery waste liquid treatment factory 3, first, the liquid is supplied to a solid-liquid separation step 4 by a solid-liquid separation device. In the solid-liquid separation step 4, the solid phase 5 (for example, 10t) and the liquid phase 6 (for example, 90t) are separated. The separated solution of the liquid phase 6 is usually 80, in the case of brewing waste liquid from the shochu manufacturing process.
A BOD value of about 000 ppm is shown.

【0013】この固液分離された溶液は、次に、濾過工
程7に供給される。濾過には、砂濾過の他、精密フィル
ターを用いた濾過、限外濾過等を適用できる。濾過によ
り、主として、固液分離工程4では分離除去し得なかっ
た溶液中のコロイド成分や多糖類成分、タンパク質成分
等が除去される。これらの成分が除去された濾過後の溶
液は、たとえば、40,000ppm程度のBOD値を
示す。
The solid-liquid separated solution is then supplied to the filtration step 7. In addition to sand filtration, filtration using a precision filter, ultrafiltration and the like can be applied to the filtration. The filtration mainly removes the colloidal component, the polysaccharide component, the protein component, etc. in the solution that could not be separated and removed in the solid-liquid separation step 4. The solution after filtration from which these components have been removed exhibits a BOD value of, for example, about 40,000 ppm.

【0014】濾過後の溶液は、電気透析工程8に供給さ
れ、電気透析により、イオン成分9、たとえば、アミノ
成分や、酢酸、クエン酸等の有機酸成分が、透析除去さ
れる(除去量:たとえば10t)。この電気透析前に、
濾過工程7でコロイド成分等が予め除去されているの
で、電気透析面等への異物の付着を抑えることができ、
電気透析処理は円滑に効率よく行われる。アミノ酸成分
等は、焼酎製造工程からの醸造廃液の場合、通常、1〜
2%程度含有されているが、電気透析により極めて精度
よく溶液中から抽出される。イオン成分9が除去された
溶液は、たとえば、30,000ppm程度のBOD値
を示す。
The solution after filtration is supplied to the electrodialysis step 8, and the ionic component 9, for example, the amino component and the organic acid component such as acetic acid and citric acid are dialyzed and removed by electrodialysis (removal amount: For example, 10t). Before this electrodialysis,
Since the colloidal components and the like have been removed in advance in the filtration step 7, it is possible to prevent foreign matter from adhering to the electrodialysis surface,
The electrodialysis treatment is performed smoothly and efficiently. Amino acid components are usually 1 to 1 in the case of brewing waste liquid from the shochu manufacturing process.
Although it is contained in about 2%, it is extracted from the solution with extremely high accuracy by electrodialysis. The solution from which the ionic component 9 has been removed exhibits a BOD value of about 30,000 ppm, for example.

【0015】イオン成分9が除去された溶液は、本実施
態様では、次に、希釈工程10で希釈され、希釈された
溶液が活性汚泥処理工程11に供給される。図示例で
は、約3倍に希釈され、希釈後のBOD値は10,00
0ppm程度とされている。活性汚泥処理工程11に
は、周知の高濃度有機廃液用活性汚泥処理設備、たとえ
ば、光合成細菌槽や曝気槽、沈殿槽、汚泥分解槽等を備
えた処理設備を用いることができる。事前に希釈されて
いるので、迅速かつ効率のよい活性汚泥処理が可能とな
り、活性汚泥処理後の処理液のBOD値を容易に30p
pm程度、さらにはそれ以下とすることができる。
In the present embodiment, the solution from which the ionic components 9 have been removed is then diluted in the dilution step 10 and the diluted solution is supplied to the activated sludge treatment step 11. In the illustrated example, the BOD value after dilution is about 3 times and the BOD value after dilution is 10,000.
It is set to about 0 ppm. In the activated sludge treatment step 11, well-known activated sludge treatment equipment for high-concentration organic waste liquid, for example, treatment equipment provided with a photosynthetic bacteria tank, an aeration tank, a sedimentation tank, a sludge decomposition tank and the like can be used. Since it is diluted in advance, it enables rapid and efficient treatment of activated sludge, and the BOD value of the treated liquid after activated sludge treatment can be easily adjusted to 30p or less.
It can be about pm or even lower.

【0016】このような低いBOD値の溶液は、処理水
として、問題を生じることなく、河川等に放流すること
ができる(放流工程12)。図示例では、約80tの処
理液が放流されることになる。このように活性汚泥処理
後の処理液のBOD値は極めて低く抑えることができる
ので、上記活性汚泥処理前の溶液希釈液の少なくとも一
部として、この活性汚泥処理後の処理液を用いることが
できる。処理液を希釈に使用することにより、別途準備
する希釈液の量を低減でき、システム全体としての効率
の向上、運転コストの低減をはかることができる。
Such a solution having a low BOD value can be discharged as a treated water into a river or the like without causing a problem (discharge step 12). In the illustrated example, about 80 ton of processing liquid is discharged. Since the BOD value of the treated liquid after the activated sludge treatment can be suppressed to an extremely low value in this way, the treated liquid after the activated sludge treatment can be used as at least a part of the solution dilution liquid before the activated sludge treatment. . By using the treatment liquid for dilution, it is possible to reduce the amount of separately prepared diluting liquid, improve the efficiency of the entire system, and reduce the operating cost.

【0017】上記のような一連の溶液処理は、図1から
も明らかな如く、固液分離から放流まで、実質的に連続
的な処理が可能である。連続的な処理により、大量の廃
液を円滑に効率よく処理することが可能になる。
As is clear from FIG. 1, the series of solution treatments as described above are capable of substantially continuous treatment from solid-liquid separation to discharge. The continuous treatment makes it possible to smoothly and efficiently treat a large amount of waste liquid.

【0018】一方、固液分離工程4で分離された固相成
分5(図示例では、10t)には、本実施態様では水分
調整剤13(図示例では、5t)が添加され、水分調整
された固相成分5が、前述の電気透析工程8での電気透
析により分離されたイオン成分9と攪拌・混合される
(攪拌・混合工程14)。この攪拌・混合においては、
pHを中性かやや酸性よりに、たとえばpH6〜7程度
に調整することが好ましい。この混合により、該混合物
は、アミノ酸や有機酸等の再利用可能な成分を比較的高
濃度に含有することになる。
On the other hand, in the present embodiment, the water content adjusting agent 13 (5 t in the illustrated example) is added to the solid phase component 5 (10 t in the illustrated example) separated in the solid-liquid separation step 4 to adjust the water content. The solid phase component 5 is stirred and mixed with the ionic component 9 separated by the electrodialysis in the electrodialysis step 8 described above (stirring / mixing step 14). In this stirring and mixing,
It is preferable to adjust the pH to, for example, about pH 6 to 7 rather than neutral or slightly acidic. By this mixing, the mixture contains a reusable component such as an amino acid or an organic acid in a relatively high concentration.

【0019】このような混合物は、必要に応じて各種用
途、たとえば家畜等の飼料原料に再利用が可能なもので
ある。本実施態様では、再利用しやすい形態とするため
に、この混合物は乾燥される(乾燥工程15)。乾燥に
より、本実施態様では約11tの飼料原料16が得られ
ている。
Such a mixture can be reused for various purposes, for example, as a feed material for livestock, if necessary. In this embodiment, the mixture is dried (drying step 15) in order to make it in a form that is easy to reuse. By drying, about 11 tons of the feed raw material 16 is obtained in this embodiment.

【0020】このように、本発明に係る醸造廃液の処理
方法においては、固液分離後の溶液を処理液として放流
できるまでに効率よく処理できるとともに、固相成分も
有効に活用し、溶液処理から派生した再利用可能な成分
を円滑に、再利用可能な形態にて回収し、全体として無
駄の無い極めて効率のよいシステムとすることが可能と
なる。
As described above, in the method for treating a brewing waste liquid according to the present invention, the solution after solid-liquid separation can be efficiently treated before it can be discharged as a treatment liquid, and the solid phase component is also effectively utilized for solution treatment. The reusable components derived from can be smoothly collected in a reusable form, and an extremely efficient system with no waste as a whole can be obtained.

【0021】[0021]

【発明の効果】以上説明したように、本発明に係る醸造
廃液の処理方法によれば、醸造廃液を放流できる水質ま
で確実にかつ効率よく処理できるとともに、廃液中に含
まれていた再利用可能な成分を効率よく分離回収でき、
必要に応じて再利用に供することができる。とくに大量
の醸造廃液が排出される焼酎製造工程からの廃液処理に
適用すれば、従来行い得なかった連続的な円滑な処理が
可能になるとともに、無駄に廃棄されていた有効成分の
再利用まで可能となる。
As described above, according to the method for treating a brewing waste liquid of the present invention, it is possible to reliably and efficiently treat the quality of water that can discharge the brewing waste liquid, and to reuse the waste water contained in the waste liquid. Various components can be separated and collected efficiently,
It can be reused if necessary. Especially when applied to the waste liquid treatment from the shochu manufacturing process where a large amount of brewing waste liquid is discharged, it enables continuous smooth processing that could not be done before and even reuses wasteful discarded active ingredients. It will be possible.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明の一実施態様に係る醸造廃液の処理方法
の工程フロー図である。
FIG. 1 is a process flow diagram of a brewing waste liquid treatment method according to an embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 醸造廃液 2 ホットチャージ車 3 醸造廃液処理工場 4 固液分離工程 5 固相(成分) 6 液相(成分) 7 濾過工程 8 電気透析工程 9 イオン成分 10 希釈工程 11 活性汚泥処理工程 12 放流工程 13 水分調整剤 14 攪拌・混合工程 15 乾燥工程 16 飼料原料 1 brewing waste liquid 2 Hot charge car 3 Brewing waste liquid treatment plant 4 Solid-liquid separation process 5 Solid phase (component) 6 Liquid phase (component) 7 Filtration process 8 electrodialysis process 9 ion components 10 Dilution process 11 Activated sludge treatment process 12 Release process 13 Moisture conditioner 14 Stirring / mixing process 15 Drying process 16 Feed ingredients

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C02F 9/00 502 C02F 9/00 502L 503C 503 504A 504 C12F 3/10 C12F 3/10 C02F 1/46 103 Fターム(参考) 4B028 AC06 AG03 AP11 AP13 AP17 AP30 4D006 GA17 KA02 KA52 KA55 KA57 KA71 KB15 KB22 PA04 PB08 PB25 PC12 4D028 AB03 BA00 4D059 AA03 AA07 BD05 BE00 BE49 CA22 CC02 DB10 4D061 DA08 DB18 DC09 EA09 EB04 EB13 FA09 FA13 FA15 ─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification code FI theme code (reference) C02F 9/00 502 C02F 9/00 502L 503C 503 504A 504 C12F 3/10 C12F 3/10 C02F 1/46 103 F-term (reference) 4B028 AC06 AG03 AP11 AP13 AP17 AP30 4D006 GA17 KA02 KA52 KA55 KA57 KA71 KB15 KB22 PA04 PB08 PB25 PC12 4D028 AB03 BA00 4D059 AA03 AA07 BD05 BE00 BE49 FA22 FB09 FA13 FA09 FA13 FA09 FB09 FA09 FB07

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 醸造廃液を固液分離する工程、該固液分
離工程により分離された溶液を濾過する工程、濾過後の
溶液を電気透析しイオン成分を分離する工程、イオン成
分が分離された溶液を活性汚泥処理する工程を含むこと
を特徴とする醸造廃液の処理方法。
1. A step of solid-liquid separating the brewing waste liquid, a step of filtering the solution separated by the solid-liquid separating step, a step of electrodialyzing the filtered solution to separate an ionic component, and a separation of an ionic component A method for treating brewing waste liquid, comprising the step of treating the solution with activated sludge.
【請求項2】 前記固液分離工程により分離された固相
成分を水分調整した後、該固相成分に前記電気透析工程
により分離されたイオン成分を混合する工程を有する、
請求項1の醸造廃液の処理方法。
2. A step of adjusting the water content of the solid phase component separated in the solid-liquid separation step, and then mixing the solid phase component with the ionic component separated in the electrodialysis step,
The method for treating brewing waste liquid according to claim 1.
【請求項3】 前記イオン成分と固相成分との混合物を
乾燥する工程を有する、請求項2の醸造廃液の処理方
法。
3. The method for treating brewing waste liquid according to claim 2, further comprising the step of drying the mixture of the ionic component and the solid phase component.
【請求項4】 前記電気透析工程によるイオン成分が分
離された溶液を、活性汚泥処理するに際し希釈する工程
を有する、請求項1ないし3のいずれかに記載の醸造廃
液の処理方法。
4. The method for treating brewery waste liquid according to claim 1, further comprising a step of diluting the solution from which the ionic components have been separated by the electrodialysis step when the activated sludge is treated.
【請求項5】 希釈液の少なくとも一部に、前記活性汚
泥処理工程からの処理液を使用する、請求項4の醸造廃
液の処理方法。
5. The method for treating brewing waste liquid according to claim 4, wherein the treatment liquid from the activated sludge treatment step is used as at least a part of the diluting liquid.
【請求項6】 前記活性汚泥処理工程からの処理液を放
流する、請求項1ないし5のいずれかに記載の醸造廃液
の処理方法。
6. The method for treating brewery waste liquid according to claim 1, wherein the treatment liquid from the activated sludge treatment step is discharged.
JP2002087900A 2002-03-27 2002-03-27 Treatment method for brewing waste liquid Pending JP2003285099A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2002087900A JP2003285099A (en) 2002-03-27 2002-03-27 Treatment method for brewing waste liquid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2002087900A JP2003285099A (en) 2002-03-27 2002-03-27 Treatment method for brewing waste liquid

Publications (1)

Publication Number Publication Date
JP2003285099A true JP2003285099A (en) 2003-10-07

Family

ID=29233937

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2002087900A Pending JP2003285099A (en) 2002-03-27 2002-03-27 Treatment method for brewing waste liquid

Country Status (1)

Country Link
JP (1) JP2003285099A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008220310A (en) * 2007-03-14 2008-09-25 Mitsui Eng & Shipbuild Co Ltd Method for recovering valuables from fermented liquid
JP2011104517A (en) * 2009-11-17 2011-06-02 Mitsui Eng & Shipbuild Co Ltd Method and system for recycling food processing residual liquid as resource
WO2014092069A1 (en) * 2012-12-12 2014-06-19 栗田工業株式会社 Feedstuff additive and mixed feedstuff
WO2014092068A1 (en) * 2012-12-12 2014-06-19 栗田工業株式会社 Method for producing material for feedstuff additive

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008220310A (en) * 2007-03-14 2008-09-25 Mitsui Eng & Shipbuild Co Ltd Method for recovering valuables from fermented liquid
JP4654210B2 (en) * 2007-03-14 2011-03-16 三井造船株式会社 Method for recovering valuable materials from fermentation broth
JP2011104517A (en) * 2009-11-17 2011-06-02 Mitsui Eng & Shipbuild Co Ltd Method and system for recycling food processing residual liquid as resource
WO2014092069A1 (en) * 2012-12-12 2014-06-19 栗田工業株式会社 Feedstuff additive and mixed feedstuff
WO2014092068A1 (en) * 2012-12-12 2014-06-19 栗田工業株式会社 Method for producing material for feedstuff additive
JP2014113130A (en) * 2012-12-12 2014-06-26 Kurita Water Ind Ltd Method of producing raw material of additive for feeding stuff
JP2014113131A (en) * 2012-12-12 2014-06-26 Kurita Water Ind Ltd Feed additive and mixed feed

Similar Documents

Publication Publication Date Title
US5514282A (en) Food processing wastewater treatment and recovery process
JP2618640B2 (en) How to reprocess spent diatomaceous earth as a filtration means
EP1060134A1 (en) Method and device for treating aqueous flows in a bioreactor, an ultrafiltration unit and a membrane filtration unit
JP2003285099A (en) Treatment method for brewing waste liquid
BE1008005A6 (en) METHOD FOR PROCESSING AND SLURRY apparatus used therewith.
EP0507416B1 (en) Method for concentrating an effluent
JP2009220047A (en) Waste water treatment method and waste water treatment device
JPH07195091A (en) Treatment of waste water discharged from washing system
JPH11221575A (en) Treatment of heavy metal ion-containing discharge water
JPH08117797A (en) Treating device for drain of cleaning water
JP2009285610A (en) Method and apparatus for treating water-soluble resin component-containing alkaline wastewater
JPS5992091A (en) Disposal of waste liquor
JP2000061495A (en) Higher level treatment of night soil and device therefor
JP2001017838A (en) Desalinating method for leachate
JPS62100494A (en) Purification of human excretion waste water by solid-liquid separation and organic fertilizer production
JP2000210677A (en) Flocculating method of sludge
JP2003169629A (en) Method for desalting soy sauce lee and installation therefor
JP2000263096A (en) Treatment of livestock excreta
JP6599104B2 (en) Main ash desalination and cement raw material production method and equipment
JPS6274498A (en) Treatment of organic sewage
JPH1057989A (en) Waste water treating device
KR200248134Y1 (en) Waste water processing apparatus of food and drink
JP2002307090A (en) Pretreatment method of liming wastewater and fixing method of carbon dioxide
JP2003001296A (en) Method for removing phosphorus in sludge
JPH0418994A (en) Treatment of organic waste water