JPS5992098A - Disposal of waste liquor containing organic substance - Google Patents
Disposal of waste liquor containing organic substanceInfo
- Publication number
- JPS5992098A JPS5992098A JP57203227A JP20322782A JPS5992098A JP S5992098 A JPS5992098 A JP S5992098A JP 57203227 A JP57203227 A JP 57203227A JP 20322782 A JP20322782 A JP 20322782A JP S5992098 A JPS5992098 A JP S5992098A
- Authority
- JP
- Japan
- Prior art keywords
- methane
- tank
- organic matter
- organic substance
- liquid
- 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
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Landscapes
- Separation Using Semi-Permeable Membranes (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Treatment Of Sludge (AREA)
Abstract
Description
【発明の詳細な説明】
本発明は動植物材料を加工する工場等から排出する有機
物を含む廃液で通常の曝気酸化処理を行うためには大址
の稀釈水の添加が必要となる1万ppm内外のBOD
(生物学的酸素要求量)を含み、またそのま−酸化処理
するためには加温、加圧を必要とし、特別の設備と処理
費用の増加を生じたり、O12素富化空気の使用などを
要する廃液や、そのま\メタン醗酵法等の嫌気性処理を
行うためには有機物や8089度が不足するよりなり
01)換算数千p plnから/万p l)m内夕1の
比較内釜−fiに発生する廃液類の省エネルギー効果の
大きい経済的で無公害な賢源化処理法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention uses waste liquid containing organic matter discharged from factories that process animal and plant materials to carry out normal aeration oxidation treatment, which requires the addition of diluted water of around 10,000 ppm. BOD of
(biological oxygen demand), and oxidation treatment requires heating and pressurization, which increases the cost of special equipment and treatment, and the use of O12-enriched air. In order to carry out anaerobic treatment such as waste liquid that requires
01) Conversion from several thousand ppln to ten thousand pl) Comparison of 10000 pl) Concerning an economical, non-polluting, and resource-friendly treatment method that has a large energy-saving effect on waste liquids generated in an inner pot.
従来無知、獣肉類、植物蛋白等のノ用土工場から発生す
る廃液類で良質の材料は肥料や飼料等の製造ケ兼ねた無
公害化処理を行っている、又稀薄な廃水例えばBOD、
2θθθp)3m以下の廃水等は空気吹込法などの酸化
処理等で浄化した上放流されている。Conventionally, it was unknown that high-quality waste liquids and materials generated from soil factories for producing meat, vegetable protein, etc. are treated to make them non-polluting as they also serve as fertilizers, feeds, etc., and dilute wastewater such as BOD, etc.
2θθθp) Wastewater of 3 m or less is purified by oxidation treatment such as air blowing method and then released.
しかしながら本発明の対象である1301)数千〜1万
p pfll内外の中碌度の廃液は上記の回収処理や、
又そのま\の状態で酸化処理ケ打つ事も経済的及び技術
的に雌か(2く、現状に於てはイ、6./θ倍に稀釈し
BOl)/θθθp pm Ja下として暖気処理を行
う。However, the target of the present invention is 1301) Several thousand to 10,000 pfll medium-quality waste liquids are subject to the above-mentioned recovery treatment,
Also, it is economically and technically unsuitable to perform oxidation treatment in the same state (2, at present, it is diluted to 6./θ times BOl) / θθθp pm Ja under warm air treatment. I do.
口・酸素又は酸素富化空気の吹込
ハ・加温しながら空気吹込
二・加圧容器内での空気吹込
等が実施されているがAづれも処理コストが高価であり
、徒らに有機物801)としての公害源を多lのエネル
キーを消費して全く無益のco2.so2及びNOx等
に酸化して放出している。(イ)の方法は多数の用水を
消費して大規模な酸化槽の建設が欠点となり、(ロ)、
に)、及び(ハ)の夫々の方法も夫々特別な設備と動力
の消費量が大きい。Blow-in of oxygen or oxygen-enriched air, Blow-in of air while heating, Blow-in of air in a pressurized container, etc. have been carried out, but these methods are expensive in processing cost, and waste organic matter 801. ) as a pollution source, consuming many liters of energy and being totally useless CO2. It is oxidized and released into SO2, NOx, etc. The disadvantage of method (a) is that it consumes a lot of water and requires construction of a large-scale oxidation tank;
Methods (2) and (3) also require special equipment and a large amount of power consumption.
現在魚類υロエ工場等で実施されている一般的な処理法
について第1図に基づbて説明すると%原料の魚滓(1
)は計量器(2)で計量し、蒸煮釜(3)に投入する。The general processing method currently implemented at fish factories, etc. is explained based on Figure 1.
) is weighed using a scale (2) and placed in the steamer (3).
約’l wcAの蒸気(4)を吹込み/J−θ“Cに加
熱した後、圧搾機(5)で脱汁する。同形物は魚粕(6
)として低温度で変質を防ぎなir<ら乾燥機(7)で
処理し、乾燥魚粕製品(8)とする。魚汁(9)は加熱
蒸気のドレンと共に遠心分離機00に送り、魚油αDを
回収し製品02Jとして外販する。油分を分離した魚汁
C13Fi貯槽に受け、多重効用缶(1り・0υ・(1
11を用−で加熱濃縮し、フィッシュソリュブルQ7)
としτ外販する。上記多重効用缶α4・四・(11に於
ける極めて低譲度の魚汁を水分309σの濃縮製品に仕
上げるためここで消費する熱量は魚滓処理工場の燃費の
7θKに達してhる。又#:発した蒸気のドレン(至)
も濃縮成分の混入によりそのま\放流できなhため浄化
槽(1値で曝気処理を付層B 01)を除去後放出する
。乾燥機(7)及び多重効用缶(14)・(lυ・(1
t9の排気は臭気カ激しく排に機(1)・12+)で集
めた上、ボイラー@で燃料(ハ)と共に焼却する。Steam (4) of about 'lwcA is blown in and heated to J-θ'C, and then the juice is removed using a press (5).
) and processed in a dryer (7) at low temperature under ir to prevent deterioration to obtain a dried fish meal product (8). The fish juice (9) is sent to the centrifuge 00 together with the heated steam drain, and the fish oil αD is recovered and sold externally as product 02J. Fish juice is collected in a C13Fi storage tank from which oil has been separated.
11 was heated and concentrated using a sieve to make fish soluble Q7).
Toshi τ will be sold outside. The amount of heat consumed in the multi-effect can α4, 4, (11) to turn the extremely low yielding fish juice into a concentrated product with a moisture content of 309σ reaches 7θK, which is the fuel consumption of a fish sludge processing factory. #: Drain of emitted steam (to)
Since it cannot be discharged as it is due to contamination with concentrated components, it is discharged after removal in a septic tank (layer B01 with aeration treatment at 1 value). Dryer (7) and multi-effect can (14)・(lυ・(1
The exhaust gas from t9 has a strong odor and is collected in machines (1) and 12+), and then incinerated together with fuel (c) in a boiler @.
前述の様に魚類加工工場では魚汁の処理法として多重効
用缶νこよる#@濃縮法が一般的に実施されて−る。こ
の場合有機物/〜、29σの魚汁を真空蒸発するが、ス
ケーリングや変質肴・防ぐため比較的低温で蒸発する。As mentioned above, the multi-effect canning #@concentration method is generally practiced as a method for treating fish juice in fish processing plants. In this case, organic matter/~29σ fish juice is vacuum evaporated, but it is evaporated at a relatively low temperature to prevent scaling and spoilage.
製品は固形物的jf; 09(f言むフイツユソリュブ
ルと称する飼料又げ肥料である。最近上記多亜効用缶に
使用する蒸発用燃料のに6騰と製品の値下りから経済的
に成立せず、工場によっては操業停止に追込まれている
)ri、魚市Jハ練製品及び缶詰工場等の廃棄物処コは
必須であゆ、社会的な問題となっている。又蒸発缶の排
気やドレンも悪臭と含有有機物の処理が必要で設備的に
も不経済な点が多い。The product is a solid feed soluble fertilizer.The price of the evaporative fuel used in the above-mentioned multi-purpose cans has recently gone up by 6,000 and the price of the product has fallen, making it economically viable. Some factories have been forced to shut down operations, and waste disposal facilities for fish paste products and canning factories are essential and have become a social problem. In addition, the exhaust gas and drain from the evaporator require treatment of foul odors and organic matter contained therein, which is often uneconomical in terms of equipment.
以上の様な比較的処理の困難な中間濃度のBODを含む
廃液は各所で発生し厳しい公害規制の対象となって匹る
。The above-mentioned waste liquid containing intermediate concentration BOD, which is relatively difficult to treat, is generated in various places and is subject to strict pollution regulations.
本発明は上記の様な従来の各種処理法の難点を解消する
ためにメタン醗酵処理f散り入れることにより含有有機
物やBODfエネルギー資源に変更させて回収する様に
なし、経済的な処理法を提供すること全目的としたもの
である。In order to overcome the drawbacks of the various conventional treatment methods as described above, the present invention provides an economical treatment method by incorporating methane fermentation treatment to convert the contained organic matter and BOD to energy resources and recover them. The entire purpose was to
次に本発明の実施例を図mlに基づ込て説明する。Next, an embodiment of the present invention will be described based on Figure ml.
動植物性材料を加工する工場で発生する廃液の中で官有
物を有効に回収できる高菌度液や、そのま\IM気処理
した方が経済的稀薄液は除きBol)約グθθθp p
mから約/万〜−万I)I)In程度含有する廃液03
を貯#J6υに集める。荒ごみ類を簡単な濾過器〔φ(
にθメツシュ金網)で除き、ポンプ(至)で限外濾過器
c(Jに圧入する。この様にして得られた濃縮魚汁・屑
は約りθθθppi11の有機物を含みメタン醗酵処理
に適当な濃度に調節して引き出す。これに種汚泥を混合
をig(至)内で混入l、て種付はケ行(へメタン醗酵
槽(ロ)に送入する。Among the waste liquids generated in factories that process animal and plant materials, excluding high-bacterial liquids that can effectively recover government property and dilute liquids that are more economical to be treated with IM air as they are.
m to about /10,000 to -10,000 I) Waste liquid containing about I) 03
Collect in storage #J6υ. A simple filter [φ(
The concentrated fish juice and scraps obtained in this way contain about θθθppi11 organic matter and are suitable for methane fermentation treatment. Adjust the concentration and draw out the sludge. Mix this with seed sludge in the ignition tank (1), and send the seeding to the methane fermentation tank (2).
限外濾廟藷(ロ)を透過した液(鴎にf^1低分子鼠の
有機物が/θ0θ〜コθθθppm存在しているので異
物の浸入ケ防止する簡単な浦過器14カを経てポンプ、
叶により約2θ〜3θ”fArlに昇圧後述浸透膜(1
1に送る。有機物は逆浸透膜(jlを透溝しないので濃
縮されて器外に集り、幽初の魚汁の貯槽c3υに加えて
処理する。透遍水の])は極めて良質の用水とI「るの
で工場内の用水槽(2)に集め再使用する。この系統か
らの排出液は出ない。The liquid that has passed through the ultrafilter (b) contains f^1 low-molecular-weight organic matter in /θ0θ~koθθθppm, so it is pumped through 14 simple filters to prevent foreign matter from entering. ,
The osmotic membrane (1
Send to 1. The organic matter is concentrated using a reverse osmosis membrane (because it does not have a channel through it, it is concentrated and collected outside the vessel, and is added to the fish juice storage tank C3υ for treatment. It is collected in a water tank (2) in the factory and reused.No effluent is produced from this system.
メタン醗酵槽C荀内では醗酵の進行が極めて早い。之は
給液中の殆んどの有機物が溶解してbるためで5通常通
性メタン菌群による有4t2!Iり1の分解と可溶化の
段階が不必要で、その筐\有機版゛化、アルコール化反
応が起るためである。生成しタアミノ酸、低級脂肪酸、
アルコール類は引続きメタン菌の作用でメタン及び炭酸
ガスに消化分解される。Fermentation progresses extremely quickly in the methane fermentation tank C. This is because most of the organic matter in the liquid supply is dissolved and b is caused by facultative methane bacteria. This is because the steps of decomposition and solubilization of I-1 are unnecessary, and the casing/organic conversion and alcoholization reactions occur. Generated tamino acids, lower fatty acids,
Alcohol is subsequently digested and decomposed into methane and carbon dioxide by the action of methane bacteria.
醗酵槽(ロ)は温度の均一化と有機物溶質とメタン菌類
の接触を計るため攪拌ポンプ(7)・(ト)を運転して
醗酵槽(ロ)内を1敞拌する。又充填されたノ・ニカム
状多層板・l−(ロ)はメタン菌が多はに付着してお杓
。The fermentation tank (B) is stirred once by operating the stirring pumps (7) and (G) in order to equalize the temperature and ensure contact between the organic solute and the methane fungi. In addition, methane bacteria adhered to the filled multi-layer board L- (b) and it became ladleful.
循環流中の有機物と接触して分解消化を早めている。醗
酵槽rrh内は隔壁禰で一分割し給液が出口に)9絡す
るのを防ぐ。It comes into contact with organic matter in the circulating flow and accelerates decomposition and digestion. The inside of the fermentation tank rrh is divided into sections by partition walls to prevent the supplied liquid from entering the outlet.
醗酵41N(2)内で生じた発生ガス■は脱流器(→で
θ’l 3’6’程度含有するH2Sを除きガスタンク
に)に貯溜する。約6θθθICca13/lr/の発
熱畦を肩する回収ガスはボイラー等に使用して燃料の節
約を計る。The generated gas (2) generated in the fermentation 41N (2) is stored in a deflow device (in a gas tank except for H2S containing about θ'l 3'6' at →). The recovered gas that covers the heating ridge of approximately 6θθθICca13/lr/ is used in boilers, etc. to save fuel.
ボイラーで発生した一部の蒸気は吹込管■から醗酵槽(
ロ)内に導入し保温用に使用するが温度は自動調節され
ている。Some of the steam generated in the boiler is transferred from the blowing pipe to the fermentation tank (
(b) It is used for heat retention, and the temperature is automatically regulated.
醗酵槽I荀から抜出す消化抜液■は先づ沈降槽(ロ)で
汚泥…を分離し、練絹汚泥をポンプに)で再循壇糸に送
り、混合器・”時で給液に混入する。沈降槽(ロ)の上
溌液争カは受槽に入り、ポンプ…で酸化槽…に送る。こ
の上7「′e、@中に残存した僅かなりOυ。Digested liquid extracted from fermentation tank I is first separated from sludge in a sedimentation tank (B), and then sent to a recirculation stage using a pump (with a pump), and then sent to a mixer and a water supply. The upper liquid content in the sedimentation tank (b) enters the receiving tank and is sent to the oxidation tank by a pump.
COD (化学的酸素要求量)は曝気処理で分解浄化し
、沈降剤6Dを添加して、攪拌槽(→で凝集せしめた後
ポンプ(→で濾過機−に送り88分(懸濁固形物)を除
去し、濾滓−はメタン醗酵槽ぐ切に投入して消化処理を
繰返し、浄化された濾液−は放流。COD (Chemical Oxygen Demand) is decomposed and purified by aeration treatment, added with sedimentation agent 6D, flocculated in a stirring tank (→), and then sent to a filter in a pump (→) for 88 minutes (suspended solids). The filtrate is poured into a methane fermentation tank and the digestion process is repeated, and the purified filtrate is discharged.
するものである。It is something to do.
本発明に使用した限外濾過器は
原料魚汁処理量 1117日 qθ℃〃
有機物濃度 /θθθθppln濃縮液有機物濃度
グθθθθppHl透過水有機物濃度 /Sθ
θppln限外濾過膜型式 チューフラー型モ
ジュール 3水膜面積 23.i”/本モジュー
ル邊過水量 −2ni”/本モジュールー日送入圧
力 にlIMtIi
分画分子量 にθθθ
であり、又逆浸透には
処理液量 31ν日 !j℃〃 有機物濃度
/θθθ〜−θθθp pHl濃度液有機物濃度 に
θθθppHl
透過水有機物濃度 /θθppHl以下逆V=腺型式
スパイラル型エレメント膜面積 ?−
/本−ニーエレメント有機物除去率95に以上
常用圧力 3θにパ、A
であり又メタン醗V孝槽は
醗酵温度 37℃士2−Q 蒸気吹込で自動調節P
)(7A;−4θ 0几P −,2θθ〜3θθm
v醗酵時間 /θ日日
間 拌 ポンプ循環
槽内モジュール ))ニカムqlJプラスチック多j
−板充填返送汚泥 槽内SSd度約5π基準で返送発生
ガス 0口47jに 00215%発熱量 6θθθk
c県?
発生量 /d/Ky−投入有機物
を使用した。The ultrafilter used in the present invention has a throughput of raw fish juice of 1117 days qθ℃〃
Organic matter concentration /θθθθppln Concentrated liquid organic matter concentration
GθθθθppHl Permeated water organic matter concentration /Sθ
θppln Ultrafiltration membrane type Teufler type module 3 Water membrane area 23. i"/percentage of water around this module -2ni"/day of this module The inlet pressure is lIMtIi, the molecular weight fraction is θθθ, and the amount of treated liquid for reverse osmosis is 31ν days! j℃〃 Organic matter concentration /θθθ~-θθθp pHl concentration Liquid organic matter concentration θθθppHl Permeate water organic matter concentration /θθppHl or less Inverted V = Gland type
Spiral type element membrane area? −
/ This - Knee element organic matter removal rate of 95 or higher, the normal pressure is 3θ, A, and the fermentation temperature of the methane tank is 37℃, 2-Q, and automatic adjustment by steam blowing.
) (7A; -4θ 0 几P −, 2θθ ~ 3θθm
v Fermentation time / θ days Stirring Pump circulation tank module )) Nikam qlJ plastic multij
- Returned sludge filled with plate Return generated gas based on SSd degree in the tank 5π 00215% calorific value 6θθθk at 0 port 47j
C prefecture? Generated amount /d/Ky - input organic matter was used.
次に従来法による結果と本発明による結果とを示す。Next, results obtained by the conventional method and results obtained by the present invention will be shown.
A、従来法による鐘1娘縮によるフィシエソ1ツユプル
製造法)処理
原料 焦線 にθt/臼魚汁 11017日 濃度 J
θθθppm燃料 A厘油(蒸煮濃縮用) L
3にβ/日用水 /θ76t/日
B6本発明による処理(原料はAと同じ)燃料 A4油
(#点用のみとなる’)/J/日用水 9ノ2
1/日
本発明は以上の様な処理法であるから、従来の処理法に
くらべ燃料が大巾に節約出来るものであり、又本発明の
システムでは給液として限外捜過透過液を供給するため
逆浸透膜法の難点である給液のAjl処理が完全に行わ
れることになり、極めて順調に稼動している。処理液の
P Hや液温も問題なく、濾過膜の逆洗や定期的な殺菌
を行う必要はあるが、濃縮液がメタン醗酵用であり、透
過水も工業用に使用するため、医槃用又は飲食用に供す
る場合のような厳電な管理は不用であり操業が極めて簡
卑になった。又大まかな有機物の分離編組用としての活
用により、従来に於て極めて処理の難しいBol)値数
千pplnから/万ppm内外の有機物を含む各地の扉
液を膜処理を主とする1i°1単な方法で濃縮し、メタ
ン醗酵法を用いて動植物性有機物をその形態をとわず消
化処理し、エネルギー化が出来る無公害処理法゛であり
、魚・鳥・獣肉等の加エエ揚や豆類処理工場の廃液、魚
類の解凍廃水処理等にも適用出来る極めて経済的な省エ
ネルギー効果の謡りものである。A. Fissieso 1 tsuyupuru production method by bell 1 daughter shrinkage according to the conventional method) Processed raw material Caustic line θt / Mortar fish juice 11017 days Concentration J
θθθppm Fuel A-lin oil (for steaming and concentration) L
3 β/Daily water /θ76t/day B6 Treatment according to the present invention (raw materials are the same as A) Fuel A4 oil (only for # point use)/J/Daily water 9 no 2
1/ Since the Japanese invention uses the above-mentioned treatment method, it can save a lot of fuel compared to the conventional treatment method, and the system of the present invention supplies the ultrasearch permeate liquid as the supply liquid. As a result, the AJL treatment of the feed liquid, which is a drawback of the reverse osmosis membrane method, has been completed completely, and the system is operating extremely smoothly. There are no problems with the pH or temperature of the treated solution, and it is necessary to backwash the filtration membrane and periodically sterilize it, but since the concentrated solution is for methane fermentation and the permeated water is also used for industrial purposes, it is a medical problem. There is no need for the strict control that would be required when using for food or drink, making the operation extremely simple. In addition, by using it for separating and braiding rough organic matter, it is possible to use 1i°1 mainly for membrane treatment of door liquids from various places containing organic matter with Bol) values ranging from several thousand ppln to 10,000 ppm, which is extremely difficult to treat in the past. It is a non-polluting processing method that can be concentrated in a simple manner and used to digest animal and plant organic matter in any form using methane fermentation and convert it into energy. It is an extremely economical and energy-saving method that can be applied to the treatment of wastewater from legume processing factories, wastewater from defrosting fish, etc.
第7図は従来の魚津加工工場の作業工程の一実施例を示
すa5a明図、第2図は本発明の一太施I71]を示す
説明図。
6カ・・濾過器、(ハ)・・限外濾過器、(@・・メタ
ン醗酵槽、(ト)・・逆浸透過膜。
出涼自大 株式会社来島グループ協同技術研9℃所
同 株式会社日本開発コンサルタント第1 図
手続補正書
昭和Sに年 −月2S日
特許庁長官 若 杉 和 夫殿
]、事件の表示
昭和 57 年 特 許 願第コθ3−2コア号2
発明の名称 有機物を含む廃液の処理法3 補正をす
る者
事件との関係 特許出願人
住所(居所) 愛媛県越智郡大西町大字新町94tS
番地(ほか1名)
6、 補正の対象 明細誓の発明の詳細な説明の項
7、補正の内容 別紙の通り
補 正 書
本願明細省第乙頁第1行目に「qθ0θ」とあるを、「
q0θθθ」とU正する。FIG. 7 is an a5a clear view showing an example of the work process of the conventional Uozu processing factory, and FIG. 2 is an explanatory view showing the first embodiment of the present invention. 6...filter, (c)...ultrafilter, (@...methane fermentation tank, (g)...reverse osmosis filtration membrane. Nihon Kaihatsu Consultant Co., Ltd. No. 1 Figure Procedure Amendment 1982-2015 Mr. Kazuo Wakasugi, Commissioner of the Patent Office], Case Indication 1982 Patent Application No. θ3-2 Core No. 2
Title of the invention Method for treating waste liquid containing organic matter 3 Relationship with the case of the person making the amendment Patent applicant address (residence) 94tS, Oaza Shinmachi, Onishi-cho, Ochi-gun, Ehime Prefecture
Address (and 1 other person) 6. Subject of amendment Section 7 of the detailed description of the invention in the specification, Contents of the amendment Amended as shown in the attached document "qθ0θ" in the first line of page 2 of the specification of the application, "
q0θθθ”.
Claims (1)
を用いて、濃縮液と透過水に分離し、濃縮液はメタン醗
酵処理を行い、含有有機物を効率よく消化してメタンガ
スを回収し、之をエネルギー諒とするとともにメタン醗
酵槽から排出する無臭化された脱離液は僅かに残存する
BOL)を曝気処理区放流し、限外藷過膜の透過水は逆
浸透膜を用いて有機物含有の濃縮液と純水とに分離し、
濃縮水はメタン醗酵槽に戻して処理分解し、透過した純
水は工場内で再利用することを特徴とする有機物を含む
廃液の処理法。Foreign substances are removed from the waste liquid using a coarse filter, and the filtrate is separated into concentrated liquid and permeated water using an ultrafiltration membrane.The concentrated liquid is subjected to methane fermentation treatment to efficiently digest the organic matter contained and generate methane gas. The deodorized desorbed liquid discharged from the methane fermentation tank is discharged into an aeration treatment area, and the water that permeates through the ultrafiltration membrane is passed through a reverse osmosis membrane. Separate into concentrated liquid containing organic matter and pure water using
A method for treating waste liquid containing organic matter, in which the concentrated water is returned to the methane fermentation tank for processing and decomposition, and the purified water that passes through is reused within the factory.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP57203227A JPS5992098A (en) | 1982-11-18 | 1982-11-18 | Disposal of waste liquor containing organic substance |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP57203227A JPS5992098A (en) | 1982-11-18 | 1982-11-18 | Disposal of waste liquor containing organic substance |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS5992098A true JPS5992098A (en) | 1984-05-28 |
Family
ID=16470554
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP57203227A Pending JPS5992098A (en) | 1982-11-18 | 1982-11-18 | Disposal of waste liquor containing organic substance |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5992098A (en) |
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS61234989A (en) * | 1985-04-12 | 1986-10-20 | Japan Organo Co Ltd | Treatment of organic waste water |
JPS62102896A (en) * | 1985-10-28 | 1987-05-13 | Hitachi Zosen Corp | Treatment of organic waste water containing colored substance |
JPH0352700A (en) * | 1989-07-18 | 1991-03-06 | Ebara Infilco Co Ltd | Treatment of sewage of night soil system |
JPH0631271A (en) * | 1992-07-16 | 1994-02-08 | Japan Organo Co Ltd | Film treatment device |
JPH11504897A (en) * | 1996-01-29 | 1999-05-11 | ロディア シミ | Process for treating aqueous liquid effluents containing organic and inorganic substances for their benefit |
CN103214111A (en) * | 2013-04-02 | 2013-07-24 | 江苏一同环保工程技术有限公司 | Wet desulphurization wastewater treatment device for limestone and gypsum |
JP2015142903A (en) * | 2013-12-26 | 2015-08-06 | 栗田工業株式会社 | Operational method of reverse osmosis membrane device and reverse osmosis membrane device |
JP2018118214A (en) * | 2017-01-26 | 2018-08-02 | オルガノ株式会社 | Method and apparatus for treating organic matter-containing wastewater |
JP2018183735A (en) * | 2017-04-25 | 2018-11-22 | 株式会社竹中工務店 | Processing method of biomass |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5684697A (en) * | 1979-12-08 | 1981-07-10 | Ebara Infilco Co Ltd | Treatment of high concentration organic waste water |
-
1982
- 1982-11-18 JP JP57203227A patent/JPS5992098A/en active Pending
Patent Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5684697A (en) * | 1979-12-08 | 1981-07-10 | Ebara Infilco Co Ltd | Treatment of high concentration organic waste water |
Cited By (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS61234989A (en) * | 1985-04-12 | 1986-10-20 | Japan Organo Co Ltd | Treatment of organic waste water |
JPS62102896A (en) * | 1985-10-28 | 1987-05-13 | Hitachi Zosen Corp | Treatment of organic waste water containing colored substance |
JPH0352700A (en) * | 1989-07-18 | 1991-03-06 | Ebara Infilco Co Ltd | Treatment of sewage of night soil system |
JPH0631271A (en) * | 1992-07-16 | 1994-02-08 | Japan Organo Co Ltd | Film treatment device |
JPH11504897A (en) * | 1996-01-29 | 1999-05-11 | ロディア シミ | Process for treating aqueous liquid effluents containing organic and inorganic substances for their benefit |
US6245121B1 (en) | 1996-01-29 | 2001-06-12 | Rhodia Chimie | Method for treating aqueous liquid effluents containing organic and inorganic materials to enable recycling thereof |
CN103214111A (en) * | 2013-04-02 | 2013-07-24 | 江苏一同环保工程技术有限公司 | Wet desulphurization wastewater treatment device for limestone and gypsum |
JP2015142903A (en) * | 2013-12-26 | 2015-08-06 | 栗田工業株式会社 | Operational method of reverse osmosis membrane device and reverse osmosis membrane device |
JP2018118214A (en) * | 2017-01-26 | 2018-08-02 | オルガノ株式会社 | Method and apparatus for treating organic matter-containing wastewater |
WO2018138970A1 (en) * | 2017-01-26 | 2018-08-02 | オルガノ株式会社 | Method and device for treating discharged water containing organic matter |
JP2018183735A (en) * | 2017-04-25 | 2018-11-22 | 株式会社竹中工務店 | Processing method of biomass |
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