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JPH11226560A - Waste liquid or wastewater treatment method and apparatus - Google Patents

Waste liquid or wastewater treatment method and apparatus

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Publication number
JPH11226560A
JPH11226560A JP3086698A JP3086698A JPH11226560A JP H11226560 A JPH11226560 A JP H11226560A JP 3086698 A JP3086698 A JP 3086698A JP 3086698 A JP3086698 A JP 3086698A JP H11226560 A JPH11226560 A JP H11226560A
Authority
JP
Japan
Prior art keywords
waste liquid
water
boiling point
tower
organic substance
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
JP3086698A
Other languages
Japanese (ja)
Inventor
Yasunori Mazaki
保徳 真崎
Takayuki Umeda
貴之 梅田
Kentaro Yoneyama
憲太郎 米山
Seiji Nomura
聖次 野村
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.)
Hitachi Ltd
Hitachi Kasado Mechanics Co Ld
Original Assignee
Hitachi Ltd
Hitachi Kasado Engineering 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 Hitachi Ltd, Hitachi Kasado Engineering Co Ltd filed Critical Hitachi Ltd
Priority to JP3086698A priority Critical patent/JPH11226560A/en
Publication of JPH11226560A publication Critical patent/JPH11226560A/en
Pending legal-status Critical Current

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  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)

Abstract

(57)【要約】 【課題】アルコール醸造におけるアルコール蒸留残査廃
液にはアルコール分が残存し、麦や芋など醗酵原料の粕
が固形分として含まれる他、他の有機物も含まれる。こ
の廃液処理が課題である。 【解決手段】そこで精溜と言う一般的な操作を使ってア
ルコールを除くことに主眼を置き廃液中の有機物を除こ
うとするものである。残存有機物の指標である生物学的
酸素要求量を減らすことができ、アルコールは不純物を
含むが有用物として回収可能となる。
(57) [Summary] [Problem] To remove alcohol distillation residue waste liquid in alcohol brewing, alcohol remains, and wastes of fermentation raw materials such as wheat and potato are contained as solids, and also other organic substances are contained. This waste liquid treatment is an issue. Therefore, the main purpose is to remove alcohol by using a general operation called rectification to remove organic substances in waste liquid. Biological oxygen demand, which is an indicator of residual organic matter, can be reduced, and alcohol can be recovered as useful, although containing impurities.

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】本発明は醸造廃液等の揮発性
有機物を含む廃液(廃水を含む)を処理する廃液処理装
置および方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus and method for treating waste liquid (including waste water) containing volatile organic substances such as brewery waste liquid.

【0002】[0002]

【従来の技術】生物学的酸素要求量(以下BODと言
う)の高い廃液を処理する従来技術としては、メタン菌
を用いた嫌気性発酵(メタン醗酵)によりBODを低下
させる方法がある。また、特殊菌を用いた好気性処理に
よるBOD低下方法もあるが、いずれも微生物処理であ
る。
2. Description of the Related Art As a conventional technique for treating a waste liquid having a high biological oxygen demand (hereinafter referred to as BOD), there is a method of reducing BOD by anaerobic fermentation (methane fermentation) using methane bacteria. There is also a method of lowering the BOD by aerobic treatment using a special bacterium.

【0003】例えば、アルコール醸造におけるアルコー
ル蒸留後の廃液は大部分が水分であるが、粕と呼ばれる
固形分の他に微量に残存するアルコール分やその他の副
生成物が含まれているため高いBODを示す。この廃液
を蒸発させた蒸気の凝縮液もアルコール等揮発分が含ま
れるため高いBODを示す。このような廃液の処理方法
の一例として図7に示す方法がある。
[0003] For example, the waste liquid after alcohol distillation in alcohol brewing is mostly water, but has a high BOD because it contains a small amount of residual alcohol and other by-products in addition to solids called lees. Is shown. The vapor condensate obtained by evaporating the waste liquid also contains a volatile component such as alcohol, and thus exhibits a high BOD. As an example of such a waste liquid treatment method, there is a method shown in FIG.

【0004】図7に示す方法は廃液を遠心分離機51で
固形分を主体とするケーキ部と濾液部とに分離し、この
分離により得られた濾液部を濃縮器53で蒸発させる。
濾液蒸発のための熱エネルギーにはケーキ部を焼却する
際に得られる排ガスの熱エネルギーを使う。濃縮液は焼
却炉55でケーキ部と共に焼却されるが、蒸発蒸気凝縮
液はメタン菌による嫌気性水処理装置57でBODを低
下させた後、活性汚泥法による好気性水処理装置59で
最終水処理を行っている。このように、蒸発蒸気凝縮液
はアルコールや他の揮発性副生成物が含まれ、BODが
10,000〜30,000ppmと高いため、特殊な
微生物処理が必要である。
In the method shown in FIG. 7, the waste liquid is separated into a cake part mainly composed of solids and a filtrate part by a centrifuge 51, and the filtrate part obtained by this separation is evaporated by a concentrator 53.
The thermal energy of the exhaust gas obtained when the cake part is incinerated is used as the thermal energy for evaporating the filtrate. The concentrated liquid is incinerated together with the cake portion in the incinerator 55. The evaporative vapor condensate is reduced in BOD by the anaerobic water treatment device 57 using methane bacteria, and then the final water is discharged in the aerobic water treatment device 59 by the activated sludge method. Processing is in progress. Thus, the evaporative vapor condensate contains alcohol and other volatile by-products and has a high BOD of 10,000 to 30,000 ppm, requiring special microbial treatment.

【0005】[0005]

【発明が解決しようとする課題】これら微生物による処
理方法は処理出来るようになるまでの微生物の初期育成
時間が長く、処理を開始後も微生物生育のため不足する
栄養源の添加を行ったり、処理中のBODの変化あるい
は処理しない時の微生物管理などが困難であるなどの問
題がある。
The treatment method using these microorganisms requires a long initial cultivation time of the microorganisms until the treatment can be carried out. Even after the treatment is started, a nutrient source which is insufficient for the growth of the microorganisms may be added or treated. There are problems such as a change in the BOD in the medium or difficulty in controlling the microorganisms when not treating.

【0006】本発明の目的は、BODの高い廃液を微生
物による処理に頼らないで、BODを低下させることが
できる廃液処理方法および装置を提供するものである。
It is an object of the present invention to provide a waste liquid treatment method and apparatus capable of reducing BOD without depending on treatment of waste liquid having a high BOD by microorganisms.

【0007】[0007]

【課題を解決するための手段】本発明では、基本的構成
として、精留作用による分離が行われる。高BODの廃
液を精溜塔により精溜し、水より沸点の低い有機物を水
を含んだ状態で溜出液として塔頂より抜き出し、塔底か
らBODの低い缶出液を得ることができる。
According to the present invention, separation by rectification is performed as a basic configuration. A waste liquid having a high BOD is rectified by a rectification column, and an organic substance having a lower boiling point than water is extracted as a distillate from the column as a distillate while containing water, and a bottom liquid having a low BOD can be obtained from the column bottom.

【0008】精溜と言う操作は低沸点物と高沸点物とを
分溜するときに使われる一般的な方法で、精溜塔の塔頂
から低沸点物を、塔底から高沸点物を分離する操作であ
る。純粋な物質を取り出したり、石油の精製に使われて
いるが、BODの高い廃液または廃水にBODを下げる
目的で使われた例はない。
[0008] The operation called rectification is a general method used for fractionating low-boiling substances and high-boiling substances. A low-boiling substance is taken from the top of the rectifying column and a high-boiling substance is taken from the bottom of the rectifying column. It is an operation to separate. It is used for extracting pure substances and refining petroleum, but it has never been used to reduce BOD in wastewater or wastewater with high BOD.

【0009】本発明は水より沸点の低い有機物を含むB
ODの高い廃液を精溜塔によって、水より沸点の低い有
機物を純粋な状態に精溜するのではなく、水を含んだ状
態で溜出液として精溜塔の塔頂より分離することによ
り、缶出液には有機物の含有量を低下させ、缶出液のB
ODを低下させることを狙うものである。
The present invention relates to B containing an organic substance having a boiling point lower than that of water.
Rather than rectifying the waste liquid having a high OD by the rectification tower to organic substances having a boiling point lower than that of water in a pure state, by separating it from the top of the rectification tower as a distillate containing water, Reduce the organic matter content in the bottoms, and
The aim is to lower the OD.

【0010】BODの高い廃液中に水より沸点の低い有
機物を含むとき精溜塔で精溜すれば水より沸点の低い有
機物が優先的に塔頂に集まり溜出液となるが、純粋な状
態にせず、水も含ませれば蒸気圧の平衡関係により他の
有機物も含まれる。水より沸点の低い有機物と共沸物を
作る有機物があればこれも溜出液に含まれる。結果とし
て塔底の缶出液にはそれらの有機物が減少したことにな
り、BODが低下する。
When an organic substance having a boiling point lower than that of water is contained in a waste liquid having a high BOD, the organic substance having a boiling point lower than that of water is collected preferentially at the top of the column if it is rectified in a rectification column. However, if water is included, other organic substances are also included due to the equilibrium relationship of the vapor pressure. Any organic substance that forms an azeotrope with an organic substance having a boiling point lower than that of water is also included in the distillate. As a result, those organic substances are reduced in the bottom product in the bottom, and the BOD is reduced.

【0011】[0011]

【発明の実施の形態】アルコール醸造におけるアルコー
ル蒸留後の廃液を処理するのに適した廃液処理装置の一
実施例を図1に示す。
DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 shows an embodiment of a waste liquid treatment apparatus suitable for treating waste liquid after alcohol distillation in alcohol brewing.

【0012】図1に示す方法は廃液を遠心分離機51で
固形分を主体とするケーキ部と濾液部とに分離し、濾液
部を濃縮器53で蒸発させる。濾液蒸発のための熱エネ
ルギーにはケーキ部を焼却した排ガスの熱エネルギーを
使う。濃縮液は焼却炉55でケーキ部と共に焼却する。
ここまでの形態は先に図7で説明した従来方法と同じで
ある。本発明では蒸発蒸気凝縮液は精溜塔61により、
塔頂からエチルアルコールを含み水とその他の有機物も
含む溜出液を取り出すことにより、塔底からはエチルア
ルコールを殆ど含まないBODの低下をした缶出液を得
る。溜出液は水とその他の有機物も含むがエチルアルコ
ールを多く含むので粗アルコールとして回収し、缶出液
はBODを更に下げるべく、従来法と同じく活性汚泥法
による好気性水処理装置59で最終水処理を行う。
In the method shown in FIG. 1, the waste liquid is separated into a cake part mainly composed of solids and a filtrate part by a centrifugal separator 51, and the filtrate part is evaporated by a concentrator 53. The thermal energy of the exhaust gas from the incineration of the cake is used as the thermal energy for evaporating the filtrate. The concentrated liquid is incinerated in the incinerator 55 together with the cake part.
The configuration up to this point is the same as the conventional method described above with reference to FIG. In the present invention, the evaporated vapor condensate is collected by the rectification column 61.
By taking out a distillate containing ethyl alcohol and also containing water and other organic substances from the top of the column, a bottom product having a reduced BOD containing almost no ethyl alcohol is obtained from the bottom of the column. The distillate contains water and other organic substances, but contains a large amount of ethyl alcohol. Therefore, the distillate is recovered as a crude alcohol, and the bottoms are finally treated with an aerobic water treatment apparatus 59 using an activated sludge method as in the conventional method to further reduce the BOD. Perform water treatment.

【0013】図2に示す方法は濃縮器53から出る蒸発
蒸気を凝縮させずに直接精溜塔に供給すること以外は図
1の例と同じ方法である。
The method shown in FIG. 2 is the same as the example of FIG. 1 except that the vapor evaporated from the concentrator 53 is supplied directly to the rectification column without being condensed.

【0014】具体実施例1:図1の具体的一例として図
3により以下詳細に説明する。
FIG. 3 shows a specific example of FIG. 1 as a specific example of FIG.

【0015】アルコール醸造におけるアルコール蒸留後
の蒸留粕固形分を含んだ廃液を遠心分離機1により、濾
液部を濾液タンク2に固形分を主体とするケーキ部をケ
ーキタンク3に分離し、ケーキ部はケーキポンプ4によ
り遠心薄膜乾燥機5に供給し蒸留粕固形分を乾燥粉体化
する。粕粉体は遠心薄膜乾燥機5の底部より取り出され
る。遠心薄膜乾燥機5による蒸発蒸気は加熱器6に導
き、濾液ポンプ7によって送られた濾液部を加熱する。
加熱された濾液部は減圧されたフラッシュタンク8に導
入され一部が蒸発する。未蒸発濾液部は循環ポンプ9で
加熱器6に繰り返し送られフラッシュタンク8で蒸発を
繰り返して濃縮される。濃縮液は濃縮液ポンプ10によ
り、ケーキタンク3に戻されケーキ部と混合されケーキ
ポンプ4により遠心薄膜乾燥機5に送られる。フラッシ
ュタンク8で蒸発した蒸気はコンデンサー11で凝縮さ
れ、非凝縮ガスがあれば真空ポンプ12により排気され
る。凝縮液は凝縮液タンク13に受けられ、第1凝縮液
ポンプ14により真空中より抜き出され、精溜塔16の
中間部に供給される。一方加熱器6で加熱に使われた蒸
気の凝縮液も第2凝縮液ポンプ15により精溜塔16の
中間部に供給される。精溜塔16では底部に吹き込まれ
たスチームにより、低沸点のアルコールが塔底側から追
い出される形で塔頂側に移動し、精溜塔16の塔頂から
アルコール等が水分と共に蒸気として出て、塔頂コンデ
ンサー17で凝縮され、溜出タンク18を経て精溜塔1
6の塔頂に還流される。アルコール分が多い液が還流さ
れることにより塔頂のアルコール分はますます濃度が高
くなる。目標のアルコール濃度に達した溜出液は一部抜
き取り粗アルコールとして回収する。一方精溜塔16底
部から排出される缶出液は水より沸点の低い有機物は殆
どなくBODは大幅に低下しているが、沸点の高い有機
物は含まれるので好気性水処理装置により更にBODを
下げるべく処理する。
In the alcohol brewing, the waste liquid containing the solid content of the distilled cake after alcohol distillation is separated by a centrifugal separator 1 into a filtrate tank 2 and a cake part mainly composed of solids into a cake tank 3. Is supplied to the centrifugal thin-film dryer 5 by the cake pump 4 to dry and solidify the distillation residue solids. The cake powder is taken out from the bottom of the centrifugal thin film dryer 5. The vapor evaporated by the centrifugal thin film dryer 5 is led to the heater 6 to heat the filtrate part sent by the filtrate pump 7.
The heated filtrate is introduced into the depressurized flash tank 8 and a part thereof is evaporated. The non-evaporated filtrate is repeatedly sent to the heater 6 by the circulation pump 9 and repeatedly evaporated in the flash tank 8 to be concentrated. The concentrate is returned to the cake tank 3 by the concentrate pump 10, mixed with the cake part, and sent to the centrifugal thin film dryer 5 by the cake pump 4. The vapor evaporated in the flash tank 8 is condensed in the condenser 11, and any non-condensed gas is exhausted by the vacuum pump 12. The condensate is received by the condensate tank 13, extracted from the vacuum by the first condensate pump 14, and supplied to an intermediate portion of the rectification column 16. On the other hand, the vapor condensate used for heating in the heater 6 is also supplied to the intermediate part of the rectification column 16 by the second condensate pump 15. In the rectification column 16, the steam blown into the bottom moves the low-boiling alcohol to the column top side in a manner to be expelled from the column bottom side. , Condensed in the top condenser 17, passed through the distilling tank 18,
Refluxed to the top of column 6. As the alcohol-rich liquid is refluxed, the concentration of alcohol at the top of the column becomes higher and higher. A part of the distillate that has reached the target alcohol concentration is withdrawn and recovered as crude alcohol. On the other hand, the bottoms discharged from the bottom of the rectification column 16 have almost no organic matter having a lower boiling point than water, and the BOD is greatly reduced. However, since the organic matter having a high boiling point is contained, the BOD is further removed by an aerobic water treatment apparatus. Process to lower.

【0016】麦焼酎蒸留後の蒸留粕固形分を含んだ廃液
を遠心薄膜乾燥機5で蒸発させた蒸気の凝縮液はBOD
が21,000ppmあり、エチルアルコール濃度が
0.7重量%あったが、精溜塔16により底部缶出液の
BODは3,500ppmに低下した。ちなみに精溜塔
16の入口での凝縮液量1500ccを処理してエチル
アルコール37.4重量%の溜出液28ccが得られ、
この溜出液中にはその他の有機物も多種含まれていた。
The condensate of the steam obtained by evaporating the waste liquid containing the solid content of the distilled lees after the distillation of wheat shochu by the centrifugal thin film dryer 5 is BOD
Was 21,000 ppm, and the ethyl alcohol concentration was 0.7% by weight, but the BOD of the bottom bottom liquid was reduced to 3,500 ppm by the rectification column 16. By the way, 1500 cc of the condensate at the inlet of the rectification tower 16 was treated to obtain 28 cc of a distillate of 37.4% by weight of ethyl alcohol,
The distillate contained many other organic substances.

【0017】具体実施例2:図2の具体的一例として図
4に示し以下詳細に説明する。
Embodiment 2 FIG. 4 shows a specific example of FIG. 2 and will be described in detail below.

【0018】アルコール醸造におけるアルコール蒸留後
の蒸留粕固形分を含んだ廃液を遠心分離機1により、濾
液部を濾液タンク2に固形分を主体とするケーキ部をケ
ーキタンク3に分離し、ケーキ部はケーキポンプ4によ
り焼却器19により焼却する。焼却器19の燃焼排ガス
は熱交換器20で濾液ポンプ7によって送られた濾液部
を加熱し排出される。加熱された濾液部は蒸発タンク2
1に導入され一部が蒸発する。未蒸発濾液部は循環ポン
プ9で熱交換器20に繰り返し送られ蒸発タンク21で
蒸発を繰り返して濃縮される。濃縮液は濃縮液ポンプ1
0により、ケーキタンク3に戻されケーキ部と混合され
ケーキポンプ4により焼却器19に送られる。蒸発タン
ク21で蒸発した蒸気は精溜塔22の中間部に供給され
る。蒸気は精溜塔22の塔頂に行くにつれて低沸点物の
アルコール濃度が高まり、精溜塔22の塔頂からアルコ
ール等が水分と共に蒸気として出て、塔頂コンデンサー
17で凝縮され、溜出タンク18を経て精溜塔22の塔
頂に還流される。アルコール分が多い液が還流されるこ
とにより塔頂のアルコール分はますます濃度が高くな
る。目標のアルコール濃度に達した溜出液は一部抜き取
り粗アルコールとして回収する。一方液側は精溜塔22
の塔底側に行くにつれて塔底部に吹き込まれたスチーム
により、低沸点物が追い出される形で塔底側に移動し、
精溜塔22底部から排出される缶出液は水より沸点の低
い有機物は殆どなくBODは大幅に低下している。しか
しながら沸点の高い有機物は含まれるので好気性水処理
装置により更にBODを下げるべく処理する。
The waste liquid containing the solid content of the distilled cake after alcohol distillation in alcohol brewing is separated by a centrifugal separator 1 into a filtrate tank 2 and a cake part mainly composed of solids into a cake tank 3. Is incinerated by the cake pump 4 by the incinerator 19. The flue gas from the incinerator 19 is heated by the heat exchanger 20 to heat the filtrate sent by the filtrate pump 7 and discharged. The heated filtrate part is the evaporation tank 2
It is introduced into 1 and a part evaporates. The non-evaporated filtrate is repeatedly sent to the heat exchanger 20 by the circulation pump 9 and concentrated by repeating evaporation in the evaporation tank 21. Concentrate is concentrate pump 1
Due to 0, it is returned to the cake tank 3 and mixed with the cake part and sent to the incinerator 19 by the cake pump 4. The vapor evaporated in the evaporation tank 21 is supplied to an intermediate portion of the rectification tower 22. As the vapor goes to the top of the rectification tower 22, the alcohol concentration of the low-boiling substances increases, and alcohol and the like exit from the top of the rectification tower 22 as steam together with moisture, and are condensed in the top condenser 17 and the distillation tank The mixture is returned to the top of the rectification column 22 via 18. As the alcohol-rich liquid is refluxed, the concentration of alcohol at the top of the column becomes higher and higher. A part of the distillate that has reached the target alcohol concentration is withdrawn and recovered as crude alcohol. On the other hand, the liquid side is
With the steam blown into the bottom of the tower as it goes to the bottom of the tower, it moves to the bottom of the tower in such a way that low-boiling substances are expelled,
The bottoms discharged from the bottom of the rectification tower 22 have almost no organic matter having a lower boiling point than water, and the BOD is greatly reduced. However, since an organic substance having a high boiling point is contained, it is treated by an aerobic water treatment apparatus to further reduce the BOD.

【0019】具体実施例3:図5は図4の遠心分離を必
要としない例である。
Embodiment 3 FIG. 5 shows an example in which the centrifugal separation shown in FIG. 4 is not required.

【0020】アルコール醸造におけるアルコール蒸留後
の廃液は直接熱交換器20に送られ、焼却器19の燃焼
排ガスと熱交換され加熱される。加熱された廃液は蒸発
タンク21に導入され一部が蒸発する。未蒸発濾液部は
循環ポンプ9で熱交換器20に繰り返し送られ蒸発タン
ク21で蒸発を繰り返して濃縮される。濃縮液は濃縮液
ポンプ10により焼却器19に送られ焼却する。焼却器
19の燃焼排ガスは熱交換器20で廃液及び循環液と熱
交換して排出される。蒸発タンク21以降は実施例2の
図4と同様に精溜されBODの低い缶出液を得る。
The waste liquid after alcohol distillation in alcohol brewing is sent directly to the heat exchanger 20 where it is exchanged with the combustion exhaust gas of the incinerator 19 and heated. The heated waste liquid is introduced into the evaporation tank 21 and a part thereof is evaporated. The non-evaporated filtrate is repeatedly sent to the heat exchanger 20 by the circulation pump 9 and concentrated by repeating evaporation in the evaporation tank 21. The concentrate is sent to the incinerator 19 by the concentrate pump 10 and incinerated. The combustion exhaust gas from the incinerator 19 exchanges heat with the waste liquid and the circulating liquid in the heat exchanger 20 and is discharged. After the evaporating tank 21, rectification is performed in the same manner as in FIG.

【0021】具体実施例4:図2の最も簡単な具体例と
して図6で説明する。
Embodiment 4 FIG. 6 shows a simplest embodiment of FIG.

【0022】アルコール醸造におけるアルコール蒸留後
の蒸留粕固形分を含んだ廃液は遠心薄膜乾燥機5に供給
し蒸留粕固形分を乾燥粉体化する。粕粉体は遠心薄膜乾
燥機5の底部より取り出される。遠心薄膜乾燥機5から
出る蒸発蒸気は精溜塔22の中間部に供給される。以降
は実施例2の図4と同様に精溜されBODの低い缶出液
を得る。
The waste liquid containing the distilled solids after alcohol distillation in the alcohol brewing is supplied to the centrifugal thin film dryer 5 to dry the solids of the dried solids into powder. The cake powder is taken out from the bottom of the centrifugal thin film dryer 5. The vapor evaporated from the centrifugal thin film dryer 5 is supplied to an intermediate portion of the rectification tower 22. Thereafter, it is rectified in the same manner as in FIG. 4 of Example 2 to obtain a bottom liquid having a low BOD.

【0023】[0023]

【発明の効果】本発明は微生物による処理ではなく物理
的にBODを低下させるため、面倒な微生物管理が必要
なく、いつでもすぐに安定したBOD低下を実施でき
る。BODの原因成分には揮発性成分もあり特にアルコ
ール醸造におけるアルコール蒸留後の廃液にはエチルア
ルコールなどが0.8重量%以下ではあるが若干含まれ
ている。このエチルアルコールを水と共に蒸発分離する
ことにより他の揮発性有機物も蒸気圧相当分蒸発し、結
果的にエチルアルコール分以上のBOD低下となる。塔
頂から得られる水や他の有機物を含むエチルアルコール
は回収が可能である。
According to the present invention, since the BOD is physically reduced instead of being treated by a microorganism, troublesome management of the microorganism is not required, and a stable BOD reduction can be immediately performed at any time. There is a volatile component among the components causing the BOD, and in particular, the waste liquid after alcohol distillation in alcohol brewing contains a little but less than 0.8% by weight of ethyl alcohol and the like. By evaporating and separating this ethyl alcohol together with water, other volatile organic substances are also evaporated by an amount corresponding to the vapor pressure, and as a result, the BOD is reduced by more than the ethyl alcohol. Ethyl alcohol containing water and other organic matter obtained from the top can be recovered.

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

【図1】本発明による廃液処理装置の一実施例を示す構
成図である。
FIG. 1 is a configuration diagram showing one embodiment of a waste liquid treatment apparatus according to the present invention.

【図2】本発明による廃液処理装置の他の実施例を示す
構成図である。
FIG. 2 is a configuration diagram showing another embodiment of the waste liquid treatment apparatus according to the present invention.

【図3】本発明による廃液処理装置の他の実施例を示す
構成図である。
FIG. 3 is a configuration diagram showing another embodiment of the waste liquid treatment apparatus according to the present invention.

【図4】本発明による廃液処理装置の他の実施例を示す
構成図である。
FIG. 4 is a configuration diagram showing another embodiment of the waste liquid treatment apparatus according to the present invention.

【図5】本発明による廃液処理装置の他の実施例を示す
構成図である。
FIG. 5 is a configuration diagram showing another embodiment of the waste liquid treatment apparatus according to the present invention.

【図6】本発明による廃液処理装置の他の実施例を示す
構成図である。
FIG. 6 is a configuration diagram showing another embodiment of the waste liquid treatment apparatus according to the present invention.

【図7】従来の廃液処理装置の一例を示す構成図であ
る。
FIG. 7 is a configuration diagram illustrating an example of a conventional waste liquid treatment apparatus.

【符号の説明】[Explanation of symbols]

1…遠心分離機、2…濾液タンク、3…ケーキタンク、
4…ケーキポンプ、5…遠心薄膜乾燥機、6…加熱器、
7…濾液ポンプ、8…フラッシュタンク、9…循環ポン
プ、10…濃縮液戻しポンプ、11…コンデンサー、1
2…真空ポンプ、13…凝縮液タンク、14…凝縮液ポ
ンプ、15…第2凝縮液ポンプ、16、22…精溜塔、
17…塔頂コンデンサー、18…溜出液タンク、19…
焼却器、20…熱交換器、21…蒸発タンク。
1 ... centrifuge, 2 ... filtrate tank, 3 ... cake tank,
4: Cake pump, 5: Centrifugal thin film dryer, 6: Heater,
7: Filtrate pump, 8: Flash tank, 9: Circulation pump, 10: Concentrate return pump, 11: Condenser, 1
2 vacuum pump, 13 condensate tank, 14 condensate pump, 15 second condensate pump, 16, 22 rectification tower,
17 ... Tower condenser, 18 ... Distillate tank, 19 ...
Incinerator, 20: heat exchanger, 21: evaporation tank.

フロントページの続き (72)発明者 米山 憲太郎 山口県下松市大字東豊井794番地 日立笠 戸エンジニアリング株式会社内 (72)発明者 野村 聖次 山口県下松市大字東豊井794番地 株式会 社日立製作所笠戸工場内Continuing on the front page (72) Inventor Kentaro Yoneyama 794, Higashi-Toyoi, Kazamatsu, Kudamatsu, Yamaguchi Prefecture Inside the Hitachi Kasado Engineering Co., Ltd. Inside the factory

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】水より沸点の低い有機物を含む廃液を精溜
塔により精溜し、水より沸点の低い有機物を水を含んだ
状態で溜出液として塔頂より抜き出し、塔底から生物学
的酸素要求量の低い缶出液を得ることを特徴とする廃液
処理方法。
1. A waste liquid containing an organic substance having a boiling point lower than that of water is rectified by a rectification column, and an organic substance having a boiling point lower than that of water is extracted as a distillate from the top of the column as a distillate while containing water. A waste liquid treatment method comprising obtaining a bottom liquid having a low oxygen demand.
【請求項2】水より沸点の低い有機物を含む廃液の濃縮
または乾燥によって発生する蒸気を直接精溜塔に供給し
て精溜し、水より沸点の低い有機物を水を含んだ状態で
溜出液として塔頂より抜き出し、塔底から生物学的酸素
要求量の低い缶出液を得ることを特徴とする廃液処理方
法。
2. A method according to claim 1, wherein the vapor generated by concentrating or drying the waste liquid containing an organic substance having a boiling point lower than that of water is supplied directly to a rectification tower to rectify the organic substance, and the organic substance having a boiling point lower than that of water is distilled out. A waste liquid treatment method comprising extracting a liquid from the top of the tower as a liquid and obtaining a bottom liquid having a low biological oxygen demand from the bottom of the tower.
【請求項3】アルコール醸造におけるアルコール蒸留残
査廃液を、直接或いは濾過または遠心分離など固形分分
離後の濾液または固形分側のいずれかの蒸発または乾燥
など、蒸気発生を伴う処理方法において、その蒸気を直
接または凝縮液として、精溜塔に供給し、水より沸点の
低い有機物を水を含んだ状態で溜出液として塔頂より抜
き出し、塔底から生物学的酸素要求量の低い缶出液を得
ることを特徴とするアルコール蒸留残査廃液の処理方
法。
3. A treatment method involving the generation of steam, such as evaporation or drying of either the filtrate or the solids side after solids separation, such as filtration or centrifugation, directly or by filtration or centrifugation. Steam is supplied directly or as a condensate to the rectification tower, and organic substances having a lower boiling point than water are extracted as distillate from the top of the tower while containing water. A method for treating an alcohol distillation residue waste liquid, comprising obtaining a liquid.
【請求項4】水より沸点の低い有機物を含む廃液を精溜
する精溜塔と、水より沸点の低い有機物を水を含んだ状
態で溜出液として上記精溜塔の塔頂より抜き出す抜出手
段と、塔底から生物学的酸素要求量の低い缶出液を得る
液採取手段とからなることを特徴とする廃液処理装置。
4. A rectification column for rectifying a waste liquid containing an organic substance having a boiling point lower than that of water, and a withdrawal for extracting an organic substance having a boiling point lower than that of water as a distillate from the top of the rectification tower while containing water. A waste liquid treatment apparatus comprising: a discharge means; and a liquid collecting means for obtaining a bottom liquid having a low biological oxygen demand from the bottom of the tower.
【請求項5】水より沸点の低い有機物を含む廃液を濃縮
または乾燥させることにより蒸発蒸気を発生させる蒸気
発生手段と、発生された蒸気を直接供給される精溜塔
と、該精留塔に直接供給された蒸気を精溜して、水より
沸点の低い有機物を水を含んだ状態で溜出液として塔頂
より抜き出す抜出手段と、該精留塔の塔底から生物学的
酸素要求量の低い缶出液を得る液採取手段とからなるこ
とを特徴とする廃液処理装置。
5. A steam generating means for generating evaporated vapor by concentrating or drying a waste liquid containing an organic substance having a boiling point lower than that of water, a rectifying tower to which the generated steam is directly supplied, and a rectifying tower. Extracting means for rectifying the directly supplied steam and extracting an organic substance having a boiling point lower than that of water from the top of the column as a distillate in a state containing water, and a biological oxygen demand from the bottom of the rectification column. A waste liquid treatment apparatus comprising a liquid collecting means for obtaining a small amount of bottom liquid.
JP3086698A 1998-02-13 1998-02-13 Waste liquid or wastewater treatment method and apparatus Pending JPH11226560A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3086698A JPH11226560A (en) 1998-02-13 1998-02-13 Waste liquid or wastewater treatment method and apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3086698A JPH11226560A (en) 1998-02-13 1998-02-13 Waste liquid or wastewater treatment method and apparatus

Publications (1)

Publication Number Publication Date
JPH11226560A true JPH11226560A (en) 1999-08-24

Family

ID=12315661

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3086698A Pending JPH11226560A (en) 1998-02-13 1998-02-13 Waste liquid or wastewater treatment method and apparatus

Country Status (1)

Country Link
JP (1) JPH11226560A (en)

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KR100487609B1 (en) * 2002-06-18 2005-05-03 이석일 A livestock wastewater treatment process combining a distillation under reduced pressure with a biological treatment
JP2007010243A (en) * 2005-06-30 2007-01-18 Hitachi Ltd HEAT PUMP DEVICE AND HEAT PUMP OPERATION METHOD
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CN111470563A (en) * 2020-05-19 2020-07-31 河北拓康工程技术有限公司 DMF (dimethyl formamide) or DMAC (dimethylacetamide) waste gas and wastewater series treatment system and method
CN114100172A (en) * 2021-10-27 2022-03-01 中国石油化工股份有限公司 A kind of treatment method of chemical residue
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CN114772829A (en) * 2022-04-28 2022-07-22 西安热工研究院有限公司 Distillation-oxidation treatment system and method for organic acid chemical cleaning waste liquid of power plant boiler
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Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100487609B1 (en) * 2002-06-18 2005-05-03 이석일 A livestock wastewater treatment process combining a distillation under reduced pressure with a biological treatment
JP2007010243A (en) * 2005-06-30 2007-01-18 Hitachi Ltd HEAT PUMP DEVICE AND HEAT PUMP OPERATION METHOD
CN110790440A (en) * 2019-12-09 2020-02-14 郭玉伟 High COD high salt effluent disposal system
CN110790440B (en) * 2019-12-09 2024-03-26 郭玉伟 High COD high salt wastewater treatment system
CN111470563A (en) * 2020-05-19 2020-07-31 河北拓康工程技术有限公司 DMF (dimethyl formamide) or DMAC (dimethylacetamide) waste gas and wastewater series treatment system and method
CN114100172B (en) * 2021-10-27 2022-12-27 中国石油化工股份有限公司 Treatment method of chemical residual liquid
CN114100172A (en) * 2021-10-27 2022-03-01 中国石油化工股份有限公司 A kind of treatment method of chemical residue
CN114702184B (en) * 2022-04-08 2023-09-29 西安瑞联新材料股份有限公司 High-salt high-organic matter wastewater treatment device and method
CN114702184A (en) * 2022-04-08 2022-07-05 西安瑞联新材料股份有限公司 High-salt high-organic-matter wastewater treatment device and method
CN114772829A (en) * 2022-04-28 2022-07-22 西安热工研究院有限公司 Distillation-oxidation treatment system and method for organic acid chemical cleaning waste liquid of power plant boiler
WO2023207098A1 (en) * 2022-04-28 2023-11-02 西安热工研究院有限公司 Distillation-oxidation treatment system and method for waste liquid from organic acid chemical cleaning of power station boiler
CN115724489A (en) * 2022-11-17 2023-03-03 安徽金禾实业股份有限公司 Device and method for treating residual liquid of methanol rectifying tower
CN115724489B (en) * 2022-11-17 2023-12-08 安徽金禾实业股份有限公司 Residual liquid treatment device and treatment method for methanol rectifying tower

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