JPH07232983A - Electrolytic treatment of sewage and night soil - Google Patents
Electrolytic treatment of sewage and night soilInfo
- Publication number
- JPH07232983A JPH07232983A JP4262653A JP26265392A JPH07232983A JP H07232983 A JPH07232983 A JP H07232983A JP 4262653 A JP4262653 A JP 4262653A JP 26265392 A JP26265392 A JP 26265392A JP H07232983 A JPH07232983 A JP H07232983A
- Authority
- JP
- Japan
- Prior art keywords
- tank
- water
- sewage
- deodorization
- diaphragm
- 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
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/469—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
-
- 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
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
Landscapes
- Treating Waste Gases (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
- Physical Water Treatments (AREA)
- Treatment Of Sludge (AREA)
- Water Treatment By Electricity Or Magnetism (AREA)
- Fertilizers (AREA)
Abstract
Description
この発明は、隔膜電解によって出来た陽極室液の酸化と
酸性液と陰極室の還元性アルカリ液とアルカリ電解液に
電解塩素生成ガスを吹き込んだ次亜塩素酸塩液を酸化ア
ルカリ液として作り、これを汚水や糞汚泥物や家庭廃水
や業務用排水の悪臭ガスの脱臭洗滌水に別々に処理し
て、脱臭を行い更にこの両電極室の両液を別々に悪臭公
害物に添加せしめ、酸化と酸性中和を行いアルカリ電解
液で悪臭酸性液を中和し、中性として処理し脱臭を行う
と共に糞尿液の様なスカムケーキと汚水とを区別して尿
水を紫外線照射と共に直接電解液として、食塩、芒硝、
芳性アルカリ等の電解質を加えて汚水瀘液を電解透析す
る事によって、脱臭分解を行い脱臭した後のスカムケー
キを発酵法で乾式発酵を行い有機肥料と発酵種菌として
再利用し、汚水を発酵熱で蒸発して河川への流入を予防
することを特徴とした電解透析と発酵法とを利用した、
列車、飛行機、自動車、バス等の移動便所の汚泥もの処
理と公園、高速道路、競馬場、競輪場、競艇場、野球場
等や家庭用便所の脱臭分解発酵処理にかかる内容であ
る。一般汚水処理法としては、活性汚泥法が公知となっ
ているが多くの水を使用し、例えば、人糞尿水等の家庭
廃水処理では固形物の40倍以上の水を以て稀釈して瀑
気し、好気性菌や嫌気性菌を作用させながら長時間瀑気
するからその間に瀑気に際し発生する悪臭は公害となっ
ていた。この為。密閉した蓋体のカバーや活性炭による
脱臭処理が行われて来たのでその処理費が高価となって
いた。又、瀑気した濃縮廃水をタンクに一旦貯液する関
係からこのタンク内での悪臭が公害となっていた。そし
て、この濃縮液を更に凝集剤を入れて凝集して遠心分離
してスカムケーキと瀘別悪臭水を分離するが、このスカ
ムケーキも悪臭性が強く又瀘別した瀘液は瀑気槽に再生
利用するのでこの悪臭の強い瀘液の悪臭で瀑気処理の公
害性を改善出来なかった。そこで、本法は隔膜電解法、
即ち、電気的透析法によって陰陽両極室を隔膜で隔離し
て電解する事によって出来た陽極液の酸化性○2及び、
Hclo、Hcl、H2So4、乳酸又は、他の有機酸
の含有する酸性液と陰極室に電解によって出来たアルカ
リ液とを作り、又、苛性アルカリ電解透析器を別個に作
り陽極室の酸素ガスと陰極室のアルカリ性液と水素ガス
発生を利用してスカムケーキや汚水の脱臭浄化を行い、
又、別に芒硝を電解透析器によって陽極を鉄極や銅極と
して硫酸金属液を作り、陰極にはアルカリ液を作りこれ
らの両液を相互に区別して利用して脱臭分解を行う様に
した隔離電解液を交互に使用して酸化と還元と中和を行
い、金属イオンによって凝集性を高め消臭性を高める様
にし、或るいは、直接汚水液を紫外線照射を行いながら
電解液として処理して消臭せしめたものや高圧酸素を隔
離電解で作り、これをスカムケーキの脱臭分解に利用し
て悪臭公害を予防し有機肥料、脱臭繊維等でスカムケー
キを処理して無臭化せしめて公害性を改善せしめた方法
であるから、移動車や競輪場や他の公衆便所等の処理に
利用する時は二次公害予防に役立ち河川の汚染を改善す
る効果がある。又、この電解透析に於いて食塩芒硝水を
電解液とする時は、陽極室には酸化、酸性液ができ、特
に、食塩の場合は塩素ガスが発生するのでこれで下水液
を処理する時に先ず下水液から発生する悪臭ガスを洗滌
し更に還元性のアルカリ液で洗滌して脱臭処理を行い、
この両性の水を混合室で中和して一級フィルターで瀘別
し別の隔膜電解器で電解して脱臭中和した後、瀘別して
元の電解液に再生利用する。又、活性法に於ける瀑気処
理に於いてこの隔膜電解の陽極に鉄極を使用し、硫酸ソ
ーダー液をいれて隔膜として陰極と区別し陰極にチタン
表面に白金メッキしたものや、アルミ合金シリコン電極
を使用し電解せしめ陽極に得られた硫酸鉄液を瀑気後、
上澄液を取り去った濃原液を濃縮タンクにポンプで移行
し入れたものに添加して酸化しスカムケーキを凝集せし
めアルカリ電解液で中和したものを遠心分離機又は、フ
ィルタープレスで瀘別して固形物はバーク発酵繊維と混
合して発酵せしめ、スカムケーキを加水分解せしめた
後、有機肥料として製品化しその半分を種菌と再発酵材
料としてリサイクルする。又、濃縮タンク中のスカム濃
縮液は極めて悪臭ガスが強いので元もと酸性の強い液の
場合、例えば、ハム、ソーセージ、魚類加工の下水に於
いては隔膜電解の陰極室のアルカリ水液で中和し陽極液
を順次混合してPH価が中性な時に添加をやめる時は、
脱臭により濃縮タンク液は無臭となるが硫化物の多くは
スカムでは食塩水を電解液として隔膜電解を行い、隔膜
電解の陰極のアルカリ中に陽極室を発生する塩素ガスを
吹き込み次亜塩素酸ソーダーを作り、これを硫化物は硫
酸化して脱臭が行われる。又、アンモニアの多い水液で
は陰極室に活性炭によってアンモニアを吸着させて脱ア
ンモニアを行い、又は、陽極の硫酸液で中和して硫安に
したものを異なった電解液による隔膜電解により脱臭浄
化を行う様にした浄化法でもある。特に紫外線照射とオ
ゾンガスの吹き込みを併用する事によって公害性を無く
し、中性液として処理する特徴がある。一般公知の汚水
処理や工業廃水の処理は前述の如く、水を先ず爐別して
固形物をスクリーンで分離した後瀑気槽中にいれて嫌気
性、好気性菌をいれて空気に曝しながら水液をポンプで
循環して加水分解し、12〜18時間処理した上澄液は
清水を混合しながら放流し、濃縮液はポンプで濃縮タン
クに送り濃縮タンクに凝集剤を入れて沈殿せしめた水液
を遠心分離機で爐別して爐液は瀑気槽に送り固形物のス
カムケーキは脱水して焼却するか、土壌改良材として発
酵して脱臭して利用するものであったが、この様な活性
汚泥法は大型処理法として多くの工場の排水処理に使用
されるばかりでなく都市の下水処理や飲料の水道水にも
この方法が多く使用されている。欠点としては、瀑気槽
に於ける悪臭が周辺地域に拡さんする為近辺の住民が公
害ガス源の理由で設置に反対し、特に、濃縮タンクのス
カム槽は特に悪臭が発生し遠心分離機にかける時にも同
様の結果を生ずるので作業者の退職が多く、活性炭の脱
臭槽中に悪臭ガスを吸引せしめて悪臭を除去している
が、瀑気槽上面はカバーしていても酸化に空気の取り入
れを必要とする事から充分な脱臭が行われ難い欠点があ
ったものを本法はこれを改善した。この発明の実施要領
を図面で説明すると次ぎの如くである。This invention is a hypochlorite solution prepared by blowing electrolytic chlorine-producing gas into an oxidizing and acidic solution of an anode chamber liquid and a reducing alkaline solution and an alkaline electrolyte solution of a cathode chamber made by diaphragm electrolysis as an alkaline oxide solution, Separately treat this into odorous cleaning water for deodorizing offensive odor gas from sewage, fecal sludge, domestic wastewater, and industrial wastewater to deodorize, and then add both liquids in both electrode chambers separately to the odorous pollutants and oxidize them. And neutralize the malodorous acidic liquid with alkaline electrolyte, treat it as neutral and deodorize it, and distinguish between scum cake like sewage and sewage and urine water as an electrolyte directly with ultraviolet irradiation. , Salt, Glauber's salt,
By electrolytically dialysis the wastewater filtrate with addition of an electrolyte such as an aromatic alkali, the scum cake after deodorization and deodorization is subjected to dry fermentation by the fermentation method and reused as an organic fertilizer and fermenting inoculum to ferment the wastewater. Utilizing electrolytic dialysis and fermentation method, which is characterized by preventing heat from evaporating into the river.
It is related to sludge treatment of moving toilets such as trains, airplanes, automobiles and buses, and deodorizing decomposition fermentation treatment of parks, highways, racetracks, bicycle racetracks, boat racetracks, baseball fields, and domestic toilets. As a general wastewater treatment method, an activated sludge method is known, but a large amount of water is used. For example, in the treatment of domestic wastewater such as human excrement and urine water, it is diluted with 40 times as much water as solids and then watered. , A bad odor that is generated during a waterfall during the period of time during which the aerobic or anaerobic bacteria are acted on has been a pollution. Because of this. Since the deodorizing treatment with the cover of the closed lid and the activated carbon has been performed, the treatment cost is high. In addition, the bad odor in the tank was a pollution because the concentrated concentrated waste water that had been vaporized was once stored in the tank. Then, the concentrated liquid is further coagulated with a coagulant and centrifuged to separate the scum cake and the offensive malodorous water, but this scum cake also has a strong malodor and the filtered offal liquid is placed in a water tank. Since it is recycled, the bad odor of this strong odorous filtrate cannot improve the pollution of water treatment. Therefore, this method is a diaphragm electrolysis method,
That is, the oxidative property of the anolyte prepared by electrolyzing the positive and negative bipolar chambers with the diaphragm by electrodialysis, and
Hcl, Hcl, H2So4, lactic acid or other organic acid-containing acid solution and alkaline solution produced by electrolysis in the cathode chamber are made, and a caustic alkaline electrolysis dialyzer is made separately to make oxygen gas in the anode chamber and cathode. Uses the alkaline liquid and hydrogen gas generated in the chamber to deodorize and purify scum cake and sewage.
Separately, a sodium sulfate solution was made by using an electrolytic dialyzer using sodium sulfate as an iron pole or a copper pole, and an alkaline solution was made as a cathode, and both solutions were distinguished from each other for deodorization decomposition. Oxidation, reduction and neutralization are carried out by alternately using the electrolytic solution so that the metal ions enhance the cohesiveness and the deodorizing property, or the waste water solution is directly treated as an electrolytic solution while being irradiated with ultraviolet rays. Deodorized products and high-pressure oxygen are produced by isolation electrolysis, and this is used for deodorizing decomposition of scum cake to prevent foul odor pollution and treats scum cake with organic fertilizer, deodorant fiber etc. Since it is a method that has improved the method, it is effective in preventing secondary pollution when used for the treatment of moving vehicles, bicycle racetracks and other public toilets, and has the effect of improving pollution of rivers. In addition, when salt mirabilite water is used as an electrolytic solution in this electrolytic dialysis, an oxidizing and acidic solution is formed in the anode chamber. Particularly, in the case of salt, chlorine gas is generated. First, the offensive odor gas generated from the sewage liquid is washed and then deodorized by washing with a reducing alkaline liquid.
This amphoteric water is neutralized in the mixing chamber, filtered by a first-class filter, electrolyzed by another diaphragm electrolyzer to neutralize deodorization, and then filtered and recycled to the original electrolytic solution. In addition, when using the iron electrode as the anode of this diaphragm electrolysis in the gas treatment in the activation method, a sulfuric acid soda solution was added to distinguish it from the cathode, and the cathode was platinum-plated on the titanium surface or aluminum alloy. After the iron sulphate solution obtained from the anode was electrolyzed using a silicon electrode,
The concentrated stock solution from which the supernatant was removed was transferred to a concentration tank by a pump and added to the one that was added to oxidize it to agglomerate the scum cake and neutralize it with an alkaline electrolyte. The product is mixed with bark fermented fiber and fermented, the scum cake is hydrolyzed, and then it is commercialized as an organic fertilizer, half of which is recycled as inoculum and re-fermentation material. Also, since the scum concentrated liquid in the concentration tank has an extremely bad odor gas, when it is a liquid with a strong acid originally, for example, in the sewage of ham, sausage, and fish processing, it is an alkaline water liquid in the cathode chamber of the diaphragm electrolysis. When neutralizing and mixing the anolyte sequentially and stopping the addition when the PH value is neutral,
The concentrated tank liquid becomes odorless due to deodorization, but most of the sulfides in the scum are electrolyzed by diaphragm using saline solution as electrolyte, and chlorine gas that generates an anode chamber is blown into the alkali of the cathode of diaphragm electrolysis soda hypochlorite. The sulfide is sulphated and deodorized. In the case of water containing a lot of ammonia, ammonia is adsorbed by activated carbon in the cathode chamber for deammonia, or deodorization is performed by diaphragm electrolysis with a different electrolyte that is neutralized with sulfuric acid solution of the anode to make ammonium sulfate. It is also a purification method that is performed. In particular, it is characterized in that it is treated as a neutral liquid by eliminating the pollution by combining the ultraviolet irradiation and the blowing of ozone gas. As described above, generally known sewage treatment and industrial wastewater treatment are performed by first separating water and separating solid matter with a screen, and then putting it in a waterfall tank to put anaerobic and aerobic bacteria and exposing it to the air. Is circulated by a pump to hydrolyze, and the supernatant liquid treated for 12 to 18 hours is discharged while mixing fresh water, and the concentrated liquid is sent to a concentrated tank by a pump and a flocculating agent is put into the concentrated tank to cause precipitation. Was separated with a centrifuge and the soot was sent to a water tank to dehydrate and incinerate the solid scum cake, or it was fermented as a soil conditioner and deodorized for use. The sludge method is not only used as a large-scale treatment method for wastewater treatment of many factories, but is also widely used for urban sewage treatment and drinking tap water. On the downside, the bad smell in the waterfall tank spreads to the surrounding area, so residents in the vicinity oppose the installation because of the pollution gas source. Since the same result occurs when it is exposed to air, many workers retire, and the bad odor is removed by sucking off the bad odor gas into the deodorization tank of activated carbon. This method has improved the problem that the deodorization was difficult to be performed because it was necessary to take in. An embodiment of the present invention will be described below with reference to the drawings.
【図1】は電解槽(4)で電源(k)から直流50V〜
2Ampの電力を導線(2)(2’)から隔膜電極陽極
(3)と陰極(3’)に印加し電解槽(4)中で隔膜
(1)電解を行う。電解液は食塩又は、塩化カルシウム
の10〜25%液を使用する。陽極(3)の上部に蓄積
するCl、2は石灰乳液の循環タンク(5)で石灰に吸
着さ を作り、更に、パイプ(6)を通じて二次電解槽(7)
で陽極(3)を隔膜(1a)で隔離して陰極(3)で電
解液は一次電解槽(4)の陰極(3’)室のアルカリ性
水液をパイプ(6’)で導入して電解を行う。そして、
パイプからCl2ガスを陽極(3)の室内の電解アルカ
リ水に吹き込みNaocl、Naclを形成せしめる。
又、一次電解槽(4)の電解液はパイプ(6”)によっ
て消臭器タンク(8)に導入して多孔板(9)を通じて
水液の酸性塩酸次亜塩素、食塩水を流下し下部のパイプ
(10)から上向に糞汚水悪臭ガスを吹き込み水洗いし
硫化物をクロム酸ソーダーの入ったものや次亜塩素の入
った水で酸化しアンモニアを塩化アンモンに変化せし
め、パイプ(1)により二次フィルター(12)で爐別
し、活性炭で脱臭したものを瀑気槽(3)に送り酸化空
気として利用する。瀑気槽(3)は天蓋(14)によっ
て遮蔽し、タンク(15)から発酵菌の好気性菌と嫌気
性菌の濃縮液と酒精酵母、パパイヤ酵素をタンク(1
5’)より瀑気槽(13)に送りポンプ(16)に連結
したパイプ(17)(17’)で瀑気槽液を循環して瀑
気し、タンク(18)から過炭酸ソーダー、過酸化ソー
ダーを添加しながら脱臭しながら瀑気を8〜10時間行
い、上澄液(19)は上澄液沈殿槽(20)に流入して
フィルター(21)で瀘別した清澄液を浄化水と共に稀
釈して放出する。この瀑気槽(13)中の底部に沈積す
る濃原沈殿濃縮液(20)はポンプ(23)に連結する
パイプ(24)(24’)によって濃縮タンク(25)
に送入されてここで過酸化ソーダー、酸素ガス、オゾン
ガスを入れるか電解酸化によって脱臭し、遠心分離器
(26)によって脱水てスカムケーキをペースト状とし
て分離せしめ高圧電解酵素でスカムケーキを酸化せしめ
て脱臭して、樹皮、鋸屑、葉等の植物繊維、ベントナイ
ト、ゼオライト、フミン酸、コケ等と混合して酵素と酵
母を添加して発酵して有機肥料を作り、半分を種菌とし
て再生発酵繊維として利用し半分を有機肥料として市販
する。この遠心分離器(26)で分離した瀘液はポンプ
(27)に連結したパイプ(28)(28’)で瀑気槽
に水液を戻し瀑気液として再利用する。FIG. 1 shows an electrolytic cell (4) with a direct current of 50 V or more from a power source (k).
Electric power of 2 Amp is applied to the diaphragm electrode anode (3) and cathode (3 ') from the conductors (2) and (2') to electrolyze the diaphragm (1) in the electrolytic cell (4). As the electrolyte, salt or 10-25% calcium chloride solution is used. Cl and 2 accumulated on the upper part of the anode (3) are adsorbed on lime in the lime emulsion circulation tank (5). And the secondary electrolyzer (7) through the pipe (6)
Then, the anode (3) is isolated by the diaphragm (1a), and the electrolyte is electrolyzed at the cathode (3) by introducing the alkaline aqueous solution in the cathode (3 ') chamber of the primary electrolysis cell (4) through the pipe (6'). I do. And
Cl2 gas is blown into the electrolytic alkaline water in the chamber of the anode (3) from the pipe to form Nacl and Nacl.
Further, the electrolytic solution in the primary electrolytic cell (4) is introduced into the deodorizer tank (8) by the pipe (6 ″) and the acidic hydrochloric acid hypochlorous acid and the saline solution are flowed down through the perforated plate (9) to the lower part. The pipe (10) is blown upward with a bad smell of fecal sewage, washed with water, and the sulfide is oxidized with sodium chromate soda or water containing hypochlorite to change ammonia into ammonium chloride. Pipe (1) The secondary filter (12) is used to filter and the deodorized activated carbon is sent to the water vapor tank (3) and used as oxidizing air.The air vapor tank (3) is shielded by the canopy (14), and the tank (15) is used. ) From fermentative aerobic and anaerobic concentrates, sake yeast and papaya enzyme in a tank (1
5 ') is sent to the water vapor tank (13) and circulates the water vapor tank liquid with pipes (17) (17') connected to the pump (16) to vaporize the water, and the tank (18) is supplied with sodium carbonate and excess sodium carbonate. Water is added for 8 to 10 hours while deodorizing while adding sodium oxide, and the supernatant liquid (19) flows into the supernatant liquid precipitation tank (20) and the clear liquid filtered by the filter (21) is purified water. It is diluted with and released. The concentrated concentrate concentrate (20) deposited on the bottom of the water vapor tank (13) is concentrated by a pipe (24) (24 ') connected to a pump (23) to a concentration tank (25).
It is then sent to and deoxidized by adding sodium peroxide, oxygen gas, ozone gas or by electrolytic oxidation, and dehydrated by a centrifuge (26) to separate the scum cake as a paste, and the scum cake is oxidized by a high-voltage electrolyzing enzyme. Deodorize, mix with bark, sawdust, leaf and other plant fibers, bentonite, zeolite, humic acid, moss, etc. and add enzymes and yeast to ferment to make organic fertilizer, half of which is regenerated fermented fiber as inoculum And sell half of it as organic fertilizer. The filtrate separated by the centrifuge (26) is returned to the waterfall tank through the pipes (28) and (28 ') connected to the pump (27) and reused as the waterfall liquid.
【図2】は、瀑気槽(13)に送りこまれたフィルター
(12)からのパイプ(12’)(12”)を通じて脱
臭された空気は、パイプ(12”)の上部に連結したス
プレーに吸引器(30)の上面筐(31)の側面から吸
引器(30)の中央に吸引されてノズルを(30’)か
ら下部タンク(32)に噴射され瀑気槽(13)の上面
に噴入する吸引器(30)の側面の空間面(30’a)
(30”a)に細管(33)(33’)を通じて6〜1
0気圧のターボファン又は、コンプレッサーの圧縮空気
を圧入にして下部ノズルの間際から下部に噴射される。
そして、上部タンク(34)に紫外線ランプ(35)で
照射したオゾン水(36)を吸引器(30)の上部の上
面筐中央にパイプ(37)から導入して、脱臭を瀑気槽
中の汚水に導入する。この高圧酸素発生器(37)は1
00気圧の隔膜電解槽から成り、ステンレス燃結膜を以
て構成している。そして、陽極(40)の発生酸素ガス
を酸素吸着剤で吸着した後、タンク(34)に導入す
る。触媒(39)は水素ガス触媒でマンガン、ニッケ
ル、コバルト触媒からなっていて発生水素ガスは、触媒
(39)室から吸引排出パイプ(40)から排出せしめ
る。酸素ガス触媒(38)を経てオゾン発生機で無声放
電によって、オゾンを酸素ガス発生機の電解槽(37)
から作り、無声放電によって作った液を更に紫外線殺菌
して瀑気槽中に噴射空気と共に送りこむ。瀑気槽(1
3)の接触空気はそこ瀑気する時は脱臭されるが、スカ
ムケーキもこの高圧酸素ガスを吸入する事によって瀑気
時間を18時間から8時間に短縮せしめる事が出来る。
そして、100気圧の高圧電解では、電解効率はイオン
の輸率10倍も高くなるので生産が高まると共に、パイ
プ(41)に連結したオートクレーブ(42)にスカム
ケーキを入れて高圧酸素を圧入する時は10気圧で約1
0分間で悪臭は消臭され、発酵は殆ど無臭で森林臭のβ
ピネン臭で処理される。又、この発酵に於いてベントナ
イト100kgに水1000kgを入れて、ブドウ糖2
0kg食塩600g、燐酸カリ1.3kg、燐酸アンモ
ン1kgを入れて酵母菌を乳酸菌と共に入れ、発酵して
増殖されたものを樹皮100kgに対し、スカムケーキ
100kg、乃至10kgを入れて混合して山積みする
時は90℃まで上昇し発熱し水分85%のものが65〜
70%に減量し、窒素分はアンモニアガスとして発生す
るので電解液の(芒硝鉄陽極)で隔膜電解を行った陽極
液で中和する時は、鉄バクテリアの放線菌の多いものが
作られ、これにラヂエーション性のある希土類特にイッ
トリウム、ランタン、セリウム等の入った金属塩やウラ
ン、トリウム、ラジウムの入ったものを混合すると連作
障害はキトサンが水溶性となり、連作障害が予防され
る。この様にこの発明は、公害悪臭がすを隔膜電解によ
って夜間電力を使用するのでコストは低下される。そし
て、電解生成物による酸化還元物の利用によって悪臭ガ
スと汚水の悪臭を脱臭し、且つ、凝集を促進する事が出
来るので列車の便所の脱臭にも応用される。即ち、FIG. 2 shows the deodorized air from the filter (12) sent to the waterfall tank (13) through the pipes (12 ′) and (12 ″) to a spray connected to the upper part of the pipe (12 ″). The upper casing (31) of the aspirator (30) is sucked from the side surface of the casing (31) to the center of the aspirator (30), and the nozzle is ejected from (30 ') to the lower tank (32) onto the upper surface of the water vapor tank (13). Space surface (30'a) on the side of the suction device (30) to enter
6-1 through thin tube (33) (33 ') to (30 "a)
The compressed air of a 0-atmosphere turbo fan or compressor is press-injected, and is injected to the lower part just before the lower nozzle.
Then, the ozone water (36) irradiated to the upper tank (34) by the ultraviolet lamp (35) is introduced from the pipe (37) into the center of the upper surface casing of the aspirator (30) to remove deodorization in the water tank. Introduce it to sewage. This high pressure oxygen generator (37) has 1
It is composed of a diaphragm electrolysis cell of 00 atm and is constituted by a stainless steel fuel-bonded membrane. Then, the oxygen gas generated in the anode (40) is adsorbed by the oxygen adsorbent and then introduced into the tank (34). The catalyst (39) is a hydrogen gas catalyst and is composed of manganese, nickel and cobalt catalysts, and the generated hydrogen gas is discharged from the catalyst (39) chamber through the suction discharge pipe (40). Ozone is generated by silent discharge in the ozone generator through the oxygen gas catalyst (38), and ozone is generated in the electrolytic cell (37) of the oxygen gas generator.
The liquid produced by the silent discharge is further sterilized by ultraviolet light and sent into the waterfall tank together with the blast air. Water tank (1
The contact air of 3) is deodorized when there is waterfall, but the scum cake can also reduce the waterfall time from 18 hours to 8 hours by inhaling this high-pressure oxygen gas.
In 100 atm high-pressure electrolysis, the electrolysis efficiency is 10 times as high as the transport number of ions, so that the production is increased, and at the same time, when scum cake is put into the autoclave (42) connected to the pipe (41), high-pressure oxygen is injected. Is about 1 at 10 bar
The bad odor is deodorized in 0 minutes, fermentation is almost odorless, and the forest odor β
Treated with a pinene odor. Also, in this fermentation, 1000 kg of water was added to 100 kg of bentonite to obtain glucose 2
0 kg salt 600 g, potassium phosphate 1.3 kg, ammonium phosphate 1 kg, yeast yeast with lactic acid bacteria, fermented and grown 100 kg of bark, 100 kg of scum cake, and mixed to pile up When the temperature rises to 90 ° C and heat is generated and the water content is 85%,
Since the amount of nitrogen is reduced to 70% and the nitrogen content is generated as ammonia gas, when neutralized with the anolyte that has been subjected to diaphragm electrolysis with the electrolyte solution (iron mirabilite iron anode), a large amount of actinomycetes of iron bacteria is produced. Mixing this with a rare earth element having radiation properties, particularly yttrium, lanthanum, cerium, or a metal salt containing uranium, thorium, or radium, chitosan becomes water-soluble in the continuous cropping disorder and prevents the continuous cropping disorder. As described above, the present invention uses the nighttime electric power by the diaphragm electrolysis to pollute the bad smell, so that the cost is reduced. Further, the use of the redox product by the electrolysis product can deodorize the malodorous gas and the malodorous sewage and promote the aggregation, so that it is also applied to the deodorization of the toilet of the train. That is,
【図3】の上程図は列車内便所の配置図を示すもので、
列車の底部に取り付けたメンタンク(50)は尿水タン
クを示し、貯溜タンク(51)に糞尿汚水が貯蔵される
タンク(51)をしめしている。このタンク(51)の
上面の水液は上澄液として分離して水洗便所の水洗用に
使用し、即ち、(52a)〜(xz)便器にここに上澄
液のみが循環利用され洗滌液に使用される。この洗滌液
は上澄液をタンク(50)に移行せしめてし尿液の洗滌
水としてポンプ(54)(54’)によってパイプ(5
5)(55’)からし尿便器(53a)〜(53M)に
送られる。この列車のし尿便器(53a)〜(53M)
は電解槽(54)に於いて酸化分解されて脱臭したもの
をアルカリ電解液で中和して脱臭する。この様な方法で
行った脱臭は10日以上の循環使用に対しても脱臭作用
は引き続き、酸化還元法によって行われるので悪臭性は
ない。列車内の汚泥物は従来、次亜塩酸カルシウム、石
灰、着色料、粉体で処理して脱臭しているので、列車が
1ケ月も汚泥物をタンクに貯蔵するには多くの問題があ
り一定処理設備のある駅舎に放流して総合的に処理され
るが、処理設備の無い所では各駅舎での任意処理は制限
がある為、列車内での処理がより重要であり高圧電解器
による濃縮酸素で脱臭する必要がある。そして、食塩に
よる隔膜電解法によって硫化物の悪臭を次亜塩素酸ソー
ダーによる酸化と酸性液によるアンモニアの中和を行
い、更に、アルカリ性により有機酸や蛋白質の分解物の
処理を行い合併する事によって脱臭処理を行った後、酸
素による発酵によって二次公害を防ぎ、どの活性汚泥装
置も簡便化される。次ぎに[Fig. 3] The upper diagram shows the layout of the toilets inside the train.
A men tank (50) attached to the bottom of the train shows a urine water tank, and a storage tank (51) shows a tank (51) for storing manure and waste water. The water liquid on the upper surface of the tank (51) is separated as a supernatant liquid to be used for washing in a flush toilet, that is, (52a) to (xz) only the supernatant liquid is circulated and used as a cleaning liquid in the toilet bowl. Used for. As for this washing liquid, the supernatant liquid is transferred to the tank (50) and used as washing water for the urine liquid by the pipes (5) by the pumps (54) (54 ').
5) It is sent from (55 ') to the toilet urinals (53a) to (53M). Human toilet (53a) to (53M) of this train
Is deoxidized by being oxidatively decomposed and deodorized in the electrolytic cell (54) by neutralizing with an alkaline electrolyte. The deodorization carried out by such a method does not have a bad odor, since the deodorizing action is continuously carried out by the oxidation-reduction method even if it is circulated for 10 days or more. Conventionally, sludge in trains has been treated with calcium hypochlorite, lime, colorants, and powders to deodorize, so there are many problems in storing sludge in tanks for one month. Although it is discharged to the station building with treatment equipment for comprehensive treatment, optional treatment at each station building is limited where there is no treatment equipment, so treatment inside the train is more important and concentration by high-voltage electrolyzer It is necessary to deodorize with oxygen. Then, by the diaphragm electrolysis method using salt, the malodor of sulfide is oxidized by sodium hypochlorite and the ammonia is neutralized by an acid solution, and further, the decomposition products of organic acids and proteins are treated by alkalinity and merged. After deodorization, fermentation with oxygen prevents secondary pollution and simplifies any activated sludge system. Next
【図3】に於いて示す、上澄液タンク(50)の水液は
上澄液タンク(50)内に吊り下げた電解槽(50K)
中に隔膜(50E)を隔絶し陽極(3)陰極(3’)を
嵌挿して、電源(K)から直流電力を両極に印加して電
解液として300wの紫外線ランプ(S)を照射しなが
らポンプ(50C)からパイプ(50d)(50’d)
によって尿水の上澄液の瀘液を陽極(3)室に入れ又、
ポンプ(50f)によってパイプ(50g)(59,
g)によって尿水の上澄液の瀘液を陰極(3’)室に導
入し、食塩又は、芒硝に苛性アルカリ又は、炭酸アルカ
りを少量添加して電解せしめる。次ぎにポンプの回転を
同期電動機で調整して流量を毎分500〜1000cc
ぐらいにオーバーフローさせて、フロー口(50P)
(50’p)から陽極電解した液を又、陰極電解した液
を上澄液(原液中)に時間をおきながら流出せしめる。
この上澄液はタンク(50)の中央に於いて中仕切板
(50M)が嵌着されてポンプ(50s)(50’s)
によってパイプ(50P)(50’p)と(50L)
(50’L)によって各液を循環して撹拌し電解した酸
性酸化液のオーバーフロー電解液とアルカリ性還元液の
電解液(オーバーフローしたもの)とを混合し電解液に
よって殺菌を行った酸性酸化液で硫化物を硫酸化して発
生するアンモニア液を中和せしめる。又、無臭化反応を
行はしめ、又、アルカリ還元液で硫酸化酸化液を中和し
て中性塩水として循環する時は、無臭性はいつまでも保
持されるので長期1ケ月間の連続使用にも耐えられる
が、殺菌材を使用しないので放出も無害であり常に透明
液として放流される。そして、殺菌剤による二次公害は
無い。この装置を発酵繊維と組合せて尿水液は電解して
電解液を洗滌に利用する時は、悪臭が無いので家庭用の
便器に装置化する事も出来るばかりでなく、公園の公衆
便所や競馬場、野球場等にも使用される。糞固形物のス
カムケーキは発酵槽に送り乾燥発酵繊維と混合する時
は、繊維中のフミン化繊維と炭素粉によって消臭が行わ
れ、更に、発酵菌の乳酸菌と酵母菌に酸素特に、パパイ
ア酵素や他の蛋白質酵素のパイナップル根液やイチヂク
乳液を併用する時は、発酵と共に消臭が行われ悪臭は1
0分もたたずに消失する。又、電解質をアルカリ水とし
て高圧酸素で処理しても同様にスカムケーキは殆ど消臭
されて公害要因とはならない。FIG. 3 shows an aqueous solution of the supernatant liquid tank (50) shown in Fig. 3 which is an electrolytic cell (50K) suspended in the supernatant liquid tank (50).
While the diaphragm (50E) is isolated, the anode (3) and the cathode (3 ') are inserted, DC power is applied to both electrodes from the power source (K), and a 300w ultraviolet lamp (S) is irradiated as an electrolytic solution. Pump (50C) to pipe (50d) (50'd)
Put the filtrate of the supernatant of urine water into the anode (3) chamber by
The pipe (50g) (59,
According to g), the filtrate of the supernatant of urine water is introduced into the cathode (3 ') chamber, and a small amount of caustic alkali or alkaline carbonate is added to salt or salt cake for electrolysis. Next, the rotation of the pump is adjusted with a synchronous motor and the flow rate is 500 to 1000 cc per minute.
Overflow to about 50P
The solution subjected to anodic electrolysis from (50'p) and the solution subjected to cathodic electrolysis are allowed to flow out to the supernatant (in the undiluted solution) over a period of time.
A pump (50s) (50's) is attached to this supernatant by a partition plate (50M) fitted in the center of the tank (50).
Depending on the pipe (50P) (50'p) and (50L)
(50'L) is an acidic oxidizing solution in which each solution is circulated and stirred to be electrolyzed, and an overflow of an acidic oxidizing solution and an electrolytic solution of an alkaline reducing solution (which has overflowed) are mixed and sterilized by the electrolytic solution. Sulfate the sulfide to neutralize the ammonia solution generated. Also, when the odorless reaction is carried out and the sulfated oxidation solution is neutralized with an alkali reducing solution and circulated as neutral salt water, the odorlessness is retained forever, so it can be used continuously for a long period of one month. Although it can withstand, it is harmless because it does not use a sterilizing material and is always discharged as a transparent liquid. And there is no secondary pollution due to the germicide. When this device is combined with fermented fiber to electrolyze the urine water solution and use the electrolyte solution for washing, it does not have a foul odor, so not only can it be used as a household toilet bowl, but it can also be used as a public toilet in the park or horse racing. It is also used in fields and baseball fields. When the scum cake of fecal solids is sent to the fermenter and mixed with dry fermented fiber, dehumidification is performed by the huminated fiber and carbon powder in the fiber, and further oxygen is added to lactic acid bacteria and yeast of fermenting bacteria, especially papaya. When combined with pineapple root juice and fig milk lotion of enzymes and other protein enzymes, deodorization is performed along with fermentation and the malodor is 1
It disappears in less than 0 minutes. Also, even if the electrolyte is treated with alkaline water as high pressure oxygen, the scum cake is almost deodorized and does not cause pollution.
【図4】はドライ発酵装置の側面図をしめし、便器(6
0K)(60’K)を多数個配列したもので、便器(6
0K)(60’)で排便したものは下部の混和機(60
ha)(60’ha)上に落下し発酵樹皮粉上に落着す
る。そして、電動モータースィツチ(60l)(60’
l)が回転して発酵樹皮と糞ペーストを混和してタンク
(60b)(60’b)に混合物を送るときは、その混
合物は発酵菌タンク(60m)(60’m)から発酵菌
が添加されながら下部にスクリューコンベアー(60
i)(60’i)によってタンク(60ob)(60’
b)の底部に送られ蓄積されて空気の存在下で発酵に脱
臭乾燥されながらホッパーP(60n)(60’n)か
ら順次外部に取り出す。この取り出しは3日〜7日ぐら
いしてから取り出す方法がよく、更に、山積みして再発
酵を行うが発酵繊維貯蔵u字状タンク(60a)(6
0’a)に投入される様にスクリューコンベアー(60
g)を左右回転して前進交代を繰り返して行う様にして
u字状タンク(60a)(60’a)中で発酵を行う。
そして、(60j)の電解槽で隔膜電解した高圧酸素は
u字状タンク(60a)(60’a)に流入する様に
し、還元ガスも同様にタンクに入れる様にする。糞汚泥
物では窒素成分は5%、燐酸成分は6〜7%を含んでい
るから発酵によって窒素成分の多くはアンモニアに分解
し固定窒素成分は0.8〜1.8%くらいに低下し、6
%の窒素成分はアンモニアガスとなり空気中に気散する
ので電解に置ける陽極室の酸化、酸性を噴射せしめる時
は2〜10%芒硝を電解液とする時は、硫酸液が陽極を
鉄板とすると硫酸鉄と共に形成されるので硫化水素やメ
ルカプタンもこの酸性液で分解されメルカプタンの非反
応物は過酸化物や次亜塩素によって酸化硫酸化が行われ
る。しかし、発酵では次亜塩素酸を流入する時は、殺菌
性となり次後の発酵はストップする場合が多いので濃縮
菌を更に添加するか、始めから硫酸イオンの多い酸性液
か高圧酸素ガスの圧入によって脱臭を行うのが一般的で
ある。[Fig. 4] shows a side view of the dry fermentation device, and the toilet (6
It is an array of a large number of 0K) and 60'K.
If you defecate at 0K) (60 '), the lower mixer (60)
ha) (60'ha) and settle on fermented bark flour. Then, the electric motor switch (60l) (60 '
When l) rotates and mixes the fermented bark and fecal paste and sends the mixture to the tanks (60b) (60'b), the mixture is added with fermentative bacteria from the fermentation tank (60m) (60'm). The screw conveyor (60
i) (60'i) by tank (60ob) (60 '
It is sent to the bottom of b), accumulated, and deodorized and dried in fermentation in the presence of air while being taken out sequentially from hoppers P (60n) (60'n). It is better to take this out after about 3 to 7 days. In addition, pile up and re-fermentation is performed. The fermentation fiber storage u-shaped tank (60a) (6a
0'a) screw conveyor (60
Fermentation is carried out in the u-shaped tanks (60a) (60'a) such that g) is rotated left and right to repeat forward alternation.
Then, the high-pressure oxygen electrolyzed by the diaphragm in the electrolyzer (60j) is caused to flow into the u-shaped tanks (60a) and (60'a), and the reducing gas is also similarly put into the tank. Since fecal sludge contains 5% of nitrogen component and 6 to 7% of phosphoric acid component, most of nitrogen component is decomposed into ammonia by fermentation and fixed nitrogen component is reduced to 0.8 to 1.8%. 6
% Nitrogen component becomes ammonia gas and diffuses in the air, so when injecting oxidation or acidity of the anode chamber that can be placed in electrolysis, when 2-10% sodium sulfate is used as the electrolytic solution, the sulfuric acid solution makes the anode the iron plate. Since it is formed together with iron sulfate, hydrogen sulfide and mercaptan are also decomposed by this acidic liquid, and the non-reacted product of mercaptan is oxidized and sulphated by peroxide and hypochlorous acid. However, in the fermentation, when hypochlorous acid is introduced, it becomes bactericidal and often stops the subsequent fermentation, so further addition of concentrated bacteria is required, or an acidic liquid rich in sulfate ions or high-pressure oxygen gas is injected from the beginning. It is common to deodorize by.
【図4】に於いては常に乾燥状態に近い60%の含水率
のものが発酵に使用され、95%くらいの水分の含浸が
行われそれ以上の含水物では発酵が遅れ温度も上昇しな
いのでスクリューコンベアーで含水量を調整するのが良
い方法である。この発酵の場合アンモニアを消臭するに
は、竹の乾溜物のアルデヒドや有機酸エステルやビネン
系芳香種化合物や大豆蛋白質の乾溜物を水と分散して使
用するとアンモニアの消臭が完壁に行われる。この様な
乾式発酵法を採用すると列車や自動車、バス、飛行機等
の糞汚泥物は無水化状態で分解が行われるので、河川の
汚染は流水する汚水が発酵熱によって60〜80℃の温
度で蒸発されるので全く公害性とはならず、悪臭も発生
しない特徴がある。現在の多くは糞汚泥物を処理するに
は40倍以上の水の稀釈液を作る必要から膨大な設備費
用を要し、悪臭除去に多大な量の脱臭剤を必要とするの
で決して合理的処理法とは言えないが、列車の便所の様
に比較的新鮮な糞尿液の処理を行う時は、腐敗分解もあ
まり進行していないので悪臭の原因は吉草酸やインドー
ル汚染体等の有機物が多く消化液や生理液が少々入って
いる程度でガスも単純化したものが多いので尿水の直接
の隔膜電解は殺菌効果も兼ねて、二次的悪臭物の硫化水
素やメルカプタンの様な悪臭ガスの発生は少ないので脱
臭が容易に行われる。高圧酸素の発生ガスを10気圧の
高圧タンク中で処理すると10分位で脱臭される。又こ
の電解液は植物の鮮度保持にも利用される。従って紫外
線照射で発酵を抑えながら処理すれば良く、オゾンガス
の併用はより高い効果がある。この様に発酵処理を行え
ばより効果的で、発酵物は家庭園芸の肥料にも利用され
公園街路樹の肥料にも利用されるので一石二鳥の効果が
あがる。特に、列車では長距離輸送では隔膜電解法の陽
陰極室の酸化、還元の酸、アルカリ液によって大気の消
臭も固形物の消臭も同時に行われるので、有害薬品の使
用は一切ないから二次公害を生じないばかりでなく、琵
琶湖の水質にも糞尿液を流さない事は公害性が少なく有
害プランクトンの発生も少ない利益がある。そして、発
酵に際して、紙や他の繊維質は発酵物と混合して処理さ
れゴムやプラスチックスの雑物は除去スクリーンで分離
されるので発酵物の巨大生成物とはならないし、処理費
用が活性汚泥法では1トン処理すると15,000円も
かかるものが1トン800円くらいに圧縮され、更に、
河川水の二次清浄費は皆無であるから産業上有用な発明
である。この電解液の配合例を示すと次ぎの如くであ
る。[Fig. 4] In Fig. 4, a product with a water content of 60%, which is close to a dry state, is always used for fermentation, impregnation with water of about 95% is performed, and with a water content higher than that, fermentation does not delay and the temperature does not rise. A good way is to adjust the water content with a screw conveyor. In the case of this fermentation, to deodorize ammonia, use dry aldehyde of bamboo dry distillate, organic acid ester, binene aromatic compound, and soybean protein dry distillate to disperse the water to complete deodorization of ammonia. Done. When such a dry fermentation method is adopted, fecal sludge from trains, cars, buses, airplanes, etc. is decomposed in an anhydrous state, so river pollution is caused by the heat of fermentation of sewage flowing at 60-80 ° C. Since it is evaporated, it is not polluted at all and has the characteristic that it does not generate a bad odor. Most of the current treatments require a huge amount of equipment cost because it is necessary to prepare a dilute solution of 40 times more water to treat fecal sludge, and a large amount of deodorant is required to remove malodor, so it is never a rational treatment. This is not a law, but when treating relatively fresh excrement such as in the toilet of a train, the decomposition of rot has not progressed so much, so the cause of the foul odor is mostly organic substances such as valeric acid and indole pollutants. Most of the gas is simplified with only a small amount of digestive and physiological fluids, so direct membrane electrolysis of urine water also has a bactericidal effect, and a malodorous gas such as hydrogen sulfide or mercaptan which is a secondary malodorous substance. It is easy to deodorize since it is rare. When the generated gas of high-pressure oxygen is treated in a high-pressure tank of 10 atm, it is deodorized in about 10 minutes. This electrolyte is also used to maintain the freshness of plants. Therefore, it suffices to perform the treatment while suppressing the fermentation by ultraviolet irradiation, and the combined use of ozone gas is more effective. If the fermentation treatment is performed in this manner, the fermented product is used as a fertilizer for home gardening and also as a fertilizer for park roadside trees. Especially in long-distance transportation on trains, since the deodorization of the positive and negative electrode chambers of the diaphragm electrolysis method and the deoxidizing acid and alkaline liquid simultaneously deodorize the atmosphere and solids, there is no use of harmful chemicals. Not only does it not cause the next pollution, but it also has the benefit of not polluting the water quality of Lake Biwa and causing less harmful plankton. During fermentation, paper and other fibers are mixed with the fermented material and processed, and rubber and plastic impurities are separated by the removal screen, so it does not become a huge product of the fermented material and the processing cost is active. In the sludge method, 1 ton treatment costs 15,000 yen, but 1 ton is compressed to about 800 yen.
It is an industrially useful invention because there is no secondary cleaning cost for river water. An example of the composition of this electrolytic solution is as follows.
【例1】 食塩 5% 苛性アルカリ 1% 水又は尿水 93.97〜94% クローム酸ソーダー 0〜0.03%[Example 1] Salt 5% Caustic 1% Water or urine water 93.97-94% Sodium chromate 0-0.03%
【例2】 芒硝 5% 食塩 0.1% 水又は尿水 94.9%[Example 2] Glauber's salt 5% Salt 0.1% Water or urine water 94.9%
【例3】 苛性ソーダー又は炭酸ソーダー
5% 水 95%[Example 3] Caustic soda or carbonated soda
5% water 95%
【例4】 乳酸カルシウム又は有機酸塩 3
% 食塩又は芒硝 5% 茶、竹又は大豆乾溜物 0.03% 水又は尿水 90〜92% その他(Clo2、水、塩素酸塩) 上記の例えは次亜塩素酸生成用電解液で隔膜は弗化樹脂
膜、ポリアミド、同アミラン多孔質フィルム電圧5〜1
00volt電流密度0.1〜1アンペアー陽極チタン
金属表面白金鍍金、シリコンマンガン金属、シリコン合
金極、陰極も同様であるがステンレス極も使用されるが
芒硝使用のExample 4 Calcium lactate or organic acid salt 3
% Salt or Glauber's salt 5% Tea, bamboo or soybean dry distillate 0.03% Water or urine water 90-92% Others (Clo2, water, chlorate) The above example is a hypochlorous acid generating electrolyte and the diaphragm is Fluorine resin film, polyamide, amylan porous film Voltage 5 to 1
00volt Current density 0.1-1 Ampere Anode Titanium metal surface Platinum plating, Silicon manganese metal, Silicon alloy electrode, Cathode are similar, but stainless steel electrode is also used
【例2】では鉄板を使用して硫酸鉄イオンによって分解
と凝集性を高め、酸化反応を促進するが鉄イオンが増大
すると水質が悪くなるので、0.1〜5%濃度で作用せ
しめる。In Example 2, an iron plate is used to enhance the decomposition and cohesiveness by iron sulfate ions and accelerate the oxidation reaction, but the water quality deteriorates when the iron ions increase, so it is used at a concentration of 0.1 to 5%.
【例3】は、高圧酸素発生隔膜電解液である。Example 3 is a high pressure oxygen generating diaphragm electrolyte.
【例4】は、列車用電解液を示したもので、茶や竹や大
豆類の乾溜物でハイアルミのセラミック円管を回転しな
がら300〜400℃で加熱しながら乾溜した液を使用
した。この乾溜物は発酵を停止するので、電解消臭にの
み利用され桧、杉の乾溜物も消臭に利用される。この隔
膜電解法を採用する利点は、ガスクロストグラフィーや
センサーを使用して悪臭ガスの検知を行う時自動制限が
電気的隔膜電解器との組合せを行う時は、人件費を余り
要しない全自動的ソフト回路の設定が容易で、特に、電
解液として塩類を添加した水液を汚染水の上澄液を瀘別
して使用する時は、その都度成分系が変わるのでコンス
タントの電解を行う時の自動制御が可能となるばかりで
なく悪臭ガスの検知した時の酸化還元液の添加量の自動
制御を行うに便利である。又、特に隔膜電解に於る電解
液の選別指令に対しても電気的制御がやり易い利点があ
る。この電解処理に於いて50voltの電圧で最大電
流2アンペアーの電力を印加すると、最初0.1アンペ
アーから始まり、約15分で1アンペアーまで上昇し電
解温度は80〜90℃まで上昇し次第に電流密度は低下
するが、原液(電解質)を流しながら放流を続けて1分
間に1lの割合で電解する時は、チタン白金メッキ電極
10cm×20cm×0.1の寸法の面積のものを弗化
樹脂膜で電解する時は、電流密度は平均0.1〜0.3
アンペアー位となる。100cc/分の陽極室電解液を
流下せしめる時の電流値は0.5アンペアーに上昇す
る。又、この濃度を高めると電流値は比例して大とな
る。1トンの尿水を電解消臭するには250〜300w
/時の電力を消費する。以上の様にこの発明の特徴は隔
膜電解によって出来る両極室の酸化酸性液でガスを洗滌
しながらアルカリ性還元液で還元水洗して脱臭を行うと
共に、酸化酸性液とアルカリ還元液を汚泥水液に別々に
処理して殺菌酸化とアルカリ中和を行って脱臭した後、
発酵処理によって脱水した有機肥料を肥料として使用
し、河川に汚水を流失する事なく河川の公害を予防する
様にした、電解法と発酵法とを組合せ列車、自動車、バ
ス、飛行機等の便所や公園や道路、劇場、競馬場や家庭
用下水の糞尿水のたれ流しを予防せしめた脱臭処理法で
ある。又、殺菌性の公害薬品の使用が無く、農薬等の分
解処理も電解法と発酵法によって無公害されるのでゴル
フ場の排水にも利用され、連作障害の予防にも利用され
るから産業上、衛生上有用な発明である。[Example 4] shows an electrolytic solution for a train, in which a dry-distilled product of tea, bamboo or soybeans was used while being dried at 300 to 400 ° C while rotating a high aluminum ceramic circular tube. Since this dry matter stops fermentation, it is used only for electrolytic deodorization, and the dry matter of Japanese cypress and cedar is also used for deodorization. The advantage of adopting this diaphragm electrolysis method is that the automatic restriction when detecting bad smell gas using gas clastography or sensor does not require much labor cost when combined with electric diaphragm electrolyzer. The dynamic soft circuit is easy to set, especially when using a water solution containing salts as the electrolyte solution after separating the supernatant of the contaminated water, the component system changes each time, so the automatic electrolysis during constant electrolysis is performed. Not only is it possible to control, but it is convenient to automatically control the addition amount of the redox liquid when a malodorous gas is detected. In addition, there is an advantage that electrical control can be easily performed even with respect to an electrolytic solution selection command particularly in diaphragm electrolysis. In this electrolysis process, when a maximum current of 2 amperes was applied at a voltage of 50 volt, it started from 0.1 amperes and started to rise to 1 ampere in about 15 minutes. The electrolysis temperature rose to 80 to 90 ° C and the current density gradually increased. However, when electrolysis is performed at a rate of 1 liter per minute while continuously discharging the stock solution (electrolyte), a titanium platinum plating electrode having an area of 10 cm × 20 cm × 0.1 is fluorinated resin film. When electrolyzing, the current density is 0.1 to 0.3 on average.
Become ampere. The current value when flowing down 100 cc / min of the electrolyte solution in the anode chamber rises to 0.5 amperes. Further, if the concentration is increased, the current value becomes proportionally large. 250-300w to electrolytically deodorize 1 ton of urine water
It consumes electricity per hour. As described above, the feature of the present invention is that the gas is washed with the oxidizing acidic liquid of both polar chambers formed by diaphragm electrolysis and the deoxidization is performed by reducing water with an alkaline reducing liquid to deodorize, and the oxidizing acidic liquid and the alkaline reducing liquid are converted into sludge aqueous liquid. After separately treating and performing sterilization oxidation and alkali neutralization to deodorize,
Using an organic fertilizer dehydrated by fermentation as a fertilizer to prevent pollution of the river without draining sewage into the river, combining electrolytic method and fermentation method, toilets such as trains, cars, buses, airplanes, etc. It is a deodorizing method that prevents runoff of manure and sewage from parks, roads, theaters, racetracks, and household sewage. In addition, since there is no use of bactericidal pollution chemicals and the decomposition treatment of pesticides etc. is pollution-free by the electrolysis method and fermentation method, it is also used for drainage of golf courses and also for the prevention of continuous cropping failures. The invention is useful for hygiene.
【図1】 汚泥処理に於る電解消臭の工程図[Figure 1] Process diagram of electrolytic deodorization in sludge treatment
【図2】 瀑気槽の悪臭処理用瀑気ノズル器の工程図[Fig. 2] Process drawing of a water vapor nozzle device for treating malodor in a water vapor tank
【図3】 列車や高速道路、公衆便所等の汚水を脱水浄
化せしめた水洗便所の工程図[Fig. 3] Process drawing of flush toilets that dehydrated and purified sewage from trains, expressways, public toilets, etc.
【図4】 発酵法、糞尿処理便所の側面図[Fig. 4] Side view of the fertilization method and manure processing toilet
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01D 53/77 61/42 ZAB 6953−4D C02F 1/32 ZAB 1/46 ZAB 9344−4D 1/461 1/469 11/00 ZAB F 7446−4D 11/02 ZAB 7446−4D C05F 3/00 7537−4H 7/00 301 H 7537−4H 9/02 D 7537−4H 9344−4D C02F 1/46 101 C 9344−4D 103 ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location B01D 53/77 61/42 ZAB 6953-4D C02F 1/32 ZAB 1/46 ZAB 9344-4D 1 / 461 1/469 11/00 ZAB F 7446-4D 11/02 ZAB 7446-4D C05F 3/00 7537-4H 7/00 301 H 7537-4H 9/02 D 7537-4H 9344-4D C02F 1/46 101 C 9344-4D 103
Claims (1)
ける脱臭分解を行うに、隔膜電解を高圧で行い電解液と
して、一つは食塩塩化カルシウム、苛性ソーダー、炭酸
ソーダー、乳酸ソーダー等の水に溶解した液を使用し、
この電解液の一部を直接下水や糞尿水液の瀘液を利用し
て電解した酸性酸化液を汚泥水中に存在する硫化物の酸
化消臭を行い、ついで陰極のアルカリ液の還元液で処理
しアンモニア等のアルカリ液を陽極の酸化酸性液で処理
し、中和して消臭する酸化還元を採用し、発生する悪臭
は酸化還元両液と水で夫々別々に処理して脱臭し、スカ
ムケーキは高圧紫外線照射と隔膜電解酸素を作りこれで
処理して脱臭した後、有機繊維と混合せしめて発酵せし
め分解消臭する事によって有機肥料に利用せしめる事を
特徴とした、列車、バス、飛行機等の移動式便所の脱臭
分解と家庭排水の下水や糞尿汚泥物の脱臭分解や工場脱
臭、廃水の再生利用する隔膜電解発酵による公害ガス消
臭分解方法。As described below, in order to perform deodorization decomposition in industrial wastewater, domestic sewage and manure treatment, diaphragm electrolysis is carried out at high pressure, and as electrolytic solution, one is calcium chloride chloride, caustic soda, sodium carbonate, sodium lactate, etc. Use a liquid dissolved in water,
A portion of this electrolyte is directly electrolyzed by using the sewage or manure liquor filtrate to oxidize and deodorize the sulfides present in the sludge water, and then treat it with a reducing solution of the alkaline solution at the cathode. Ammonia and other alkaline liquids are treated with an anodic oxidation acidic liquid to neutralize and deodorize redox.The generated malodors are treated separately with redox liquid and water to deodorize and scum. The cake is characterized by being irradiated with high-pressure ultraviolet rays and produced by electrolysis oxygen in the diaphragm, treated with this to deodorize, and then mixed with organic fiber to ferment and eliminate the amount of odor, which can be used for organic fertilizer, train, bus, airplane. Deodorization decomposition of mobile toilets, etc., deodorization decomposition of domestic sewage and manure sludge, factory deodorization, and deodorization decomposition method of pollution gas by diaphragm electrolytic fermentation to reuse wastewater.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4262653A JPH07232983A (en) | 1992-08-18 | 1992-08-18 | Electrolytic treatment of sewage and night soil |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4262653A JPH07232983A (en) | 1992-08-18 | 1992-08-18 | Electrolytic treatment of sewage and night soil |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH07232983A true JPH07232983A (en) | 1995-09-05 |
Family
ID=17378768
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP4262653A Pending JPH07232983A (en) | 1992-08-18 | 1992-08-18 | Electrolytic treatment of sewage and night soil |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH07232983A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2004083129A1 (en) * | 2003-03-18 | 2004-09-30 | Minaki Advance Co. Ltd. | Treating agent for decomposing feces/urine and method of treating feces/urine through decomposition by activated microorgnisms |
-
1992
- 1992-08-18 JP JP4262653A patent/JPH07232983A/en active Pending
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2004083129A1 (en) * | 2003-03-18 | 2004-09-30 | Minaki Advance Co. Ltd. | Treating agent for decomposing feces/urine and method of treating feces/urine through decomposition by activated microorgnisms |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
EP0513352B1 (en) | Method of cleaning soil water | |
CN102139990B (en) | Ultrasonic combined waste water treatment process and system of refuse leachate | |
CN208949039U (en) | A kind of processing unit of black and odorous water | |
JPH09510651A (en) | Method for purifying medium containing organic waste | |
CN108640377A (en) | A kind of safe and efficient environment protection treating equipment of sewage | |
CN207435275U (en) | Microbiological treatment bio-toilet | |
US20130153509A1 (en) | Wastewater treatment comprising electrodissolution, flocculation and oxidation | |
CN101195501A (en) | Fecal sewage decolorizing method and device | |
CN207713593U (en) | A kind of domestic sewage processing system | |
CN204939207U (en) | A kind of livestock breeding wastewater treatment system | |
KR101982660B1 (en) | Sewage and drainage reuse system | |
JPH07232983A (en) | Electrolytic treatment of sewage and night soil | |
JPH0760290A (en) | Improved treatmet of pollited water | |
JP3163294B2 (en) | Waste chemical and biological treatment system | |
JPH11197675A (en) | Functional ceramics water catalytic treatment apparatus, functional ceramics, water treatment system utilizing the same and catalytic water use method | |
KR101853319B1 (en) | Manufacturing apparatus for liquid fertilizer deodorant of wastewater | |
JPH0731993A (en) | Deodorization treating device for waste water stock in raising, fishery and agricultural products and their processing | |
CN111718040A (en) | Method for preparing deodorant by electrolyzing concentrated solution of nanofiltration percolate of garbage | |
JP2000204629A (en) | Self-contained flush toilet | |
JP3537085B2 (en) | Superoxide ion generation method | |
JPH0819795A (en) | Purifier of deodorizable sewage | |
JPH11169884A (en) | Hydrogen sulfide using chemical synthesis-dependent organism and treatment dissolved methane | |
JP2006239626A (en) | Treatment method of waste and treatment apparatus | |
KR20040078173A (en) | Electrolysis and electro-coagulation treatment apparatus of wastewater | |
CN110937768A (en) | Method for treating sludge and deodorizing method |