JPS62239983A - Cultivation of yeast with waste water - Google Patents

Cultivation of yeast with waste water

Info

Publication number
JPS62239983A
JPS62239983A JP61080985A JP8098586A JPS62239983A JP S62239983 A JPS62239983 A JP S62239983A JP 61080985 A JP61080985 A JP 61080985A JP 8098586 A JP8098586 A JP 8098586A JP S62239983 A JPS62239983 A JP S62239983A
Authority
JP
Japan
Prior art keywords
yeast
treating step
treatment
wastewater
screen
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.)
Granted
Application number
JP61080985A
Other languages
Japanese (ja)
Other versions
JPH044867B2 (en
Inventor
Kaoru Chigusa
千種 薫
Norihisa Minegishi
嶺岸 令久
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.)
NIPPON BISEIBUTSU KAGAKU KK
Nishihara Environment Co Ltd
Original Assignee
NIPPON BISEIBUTSU KAGAKU KK
Nishihara Environmental Sanitation Research Corp
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 NIPPON BISEIBUTSU KAGAKU KK, Nishihara Environmental Sanitation Research Corp filed Critical NIPPON BISEIBUTSU KAGAKU KK
Priority to JP61080985A priority Critical patent/JPS62239983A/en
Publication of JPS62239983A publication Critical patent/JPS62239983A/en
Publication of JPH044867B2 publication Critical patent/JPH044867B2/ja
Granted legal-status Critical Current

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  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Fertilizers (AREA)
  • Fodder In General (AREA)

Abstract

PURPOSE:To increase the amount f recovered microbial cells, by keeping waste water under anaerobic condition for a given period, solubilizing and digesting glucides, filtering the treated solution through a screen to remove residues, treating the resultant filtrate with a yeast and recovering the yeast. CONSTITUTION:Waste water 1 containing much glucides frown a food factory is introduced into a solubilization and digestion treating step 2 subjected to anaerobic decomposition treatment and introduced into a screen treating step 3 to separate undercomposed fibers, etc. The filtrate is then introduced into a yeast treating step 4 kept under slightly aerobic condition by introducing air and fermented. The solution after the treatment is further introduced into a centrifugal separating step 5 and separated into concentrated microbial cells 6 and a supernatant liquid. The concentrated microbial cells 6 are then utilized for a fertilizer, etc. The separated solution after the centrifugal separation is then introduced into a catalytic oxidation treating step 7, subjected to aerobic biological treating step passed through a precipitating step and introduced into a sterilization treating step 8 to carry out disinfection in a chlorine disinfection vessel.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、各種飼料や肥料を製造するための廃水による
酵母の培養方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field] The present invention relates to a method for culturing yeast using wastewater for producing various feeds and fertilizers.

〔従来の技術〕[Conventional technology]

飼料や肥料の製造方法に関する公知技術として、例えば
特公昭60−29678号公報に見られるように、家畜
索類全可溶化消化して有機酸全生成した後、酵母を培養
して、飼料や肥料全製造する方法がある。
As a known technique for producing feed and fertilizer, for example, as seen in Japanese Patent Publication No. 60-29678, livestock cords are completely solubilized and digested to generate all organic acids, and then yeast is cultured to produce feed and fertilizer. There is a way to manufacture everything.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

j≠>i′i1P慰瓜 rの小噛帖缶IF ?’つイ慰
二牛シ鞘る飼料や肥料は、不活性SSの混入が多いため
に、蛋白質の含有率が低く、商品的価値が低かった。
j≠>i′i1P consolation r's small bite can IF? The feed and fertilizer used for the cattle were often contaminated with inert SS, so their protein content was low and their commercial value was low.

本発明は、菌体の回収量が多く、かつ不活性SSの混入
が少ない、廃水による酵母の培養方法全提供しようとす
るものである。
The present invention aims to provide a complete method for culturing yeast using wastewater, which yields a large amount of bacterial cells and reduces contamination with inactive SS.

〔問題点全解決するための手段〕[Means to solve all problems]

本発明は、廃水を所定期間(例えば1〜2日間)嫌気状
態に保持して可溶化消化する。その後、その処理液全ス
クリーンで濾過してし渣?除去する。そして、その瀘液
金酵母処理することによって酵母を回収するようにした
廃水による酵母の培養方法である。
In the present invention, wastewater is maintained in an anaerobic state for a predetermined period (for example, 1 to 2 days) to solubilize and digest it. After that, the entire treated liquid is filtered through a screen and the residue is removed. Remove. This is a method for culturing yeast using wastewater, in which yeast is recovered by treating the filtrate with gold yeast.

〔作用〕[Effect]

本発明は、廃水を可溶化消化した後に、スクリーンによ
ってし渣全除去し、その処理液(ン慮液)で酵母を培養
する方法であり、可溶化消化処理によって菌体の回収量
が多く、かつスクリーン処理によって不活性SSの混入
が少なくなる。
The present invention is a method of solubilizing and digesting wastewater, then removing all the residue using a screen, and culturing yeast in the treated solution. In addition, the screen treatment reduces the amount of inert SS mixed in.

〔実施例〕〔Example〕

以下に、本発明の廃水による酵母の培養方法の工程順全
第1図によって説明する。
The entire process sequence of the method for culturing yeast using wastewater according to the present invention will be explained below with reference to FIG.

先ず、廃水としては、糖質を多く含む食品工場廃水1を
用いる。
First, food factory wastewater 1 containing a large amount of carbohydrates is used as wastewater.

次に、上記廃水1全可溶化消化工程2へ導入する。Next, the wastewater 1 is introduced into the total solubilization and digestion step 2.

この可溶化消化工程2では、上記廃水1を可溶化消化槽
内で、例えば30℃前後で約24〜48時間程度嫌気状
態に保持する。これにより上記廃水1は一次的な嫌気分
解を受け、有機酸が虫取される。また、固形状の炭水化
物等の分解も起こり、液化される。このため、BODが
上昇し、SSは減少する。
In this solubilization and digestion step 2, the wastewater 1 is maintained in an anaerobic state at about 30° C. for about 24 to 48 hours in a solubilization and digestion tank. As a result, the wastewater 1 undergoes primary anaerobic decomposition, and organic acids are removed. In addition, solid carbohydrates and the like are decomposed and liquefied. Therefore, BOD increases and SS decreases.

次に、上記可溶化消化処理が終つ次処理fi?スクリー
ン処理工程6へ導入する。
Next, the next treatment after the above solubilization and digestion treatment fi? Introduced to screen treatment step 6.

このスクリーン処理工程6では、例えば目幅が約0.3
1uI8度の微細スクリーンによって上記処理液が濾過
され、未分解の繊維分やその他無機物のSS等が分離さ
れる。そして、スクリーンかすば、処理水によって洗浄
された後、スクリュープレスによって脱水されて、し渣
が除去される。なお脱水し渣は、焼却しても良いが、濃
縮菌体と混合して、肥料等に利用しても良い。また、洗
浄排水やスクリュープレス分離t14次の酵母処理工程
へ導入すると良い。
In this screen processing step 6, for example, the mesh width is about 0.3.
The treated liquid is filtered through a 1 uI 8 degree fine screen to separate undecomposed fibers and other inorganic substances such as SS. After the screen is washed with treated water, it is dehydrated using a screw press to remove the residue. Note that the dehydrated residue may be incinerated, or may be mixed with concentrated bacterial cells and used as fertilizer or the like. It is also good to introduce it into the washing waste water or the screw press separation t14 next yeast treatment step.

次に、上記スクリーン処理された濾液全酵母処理工程4
へ導入する。
Next, the screen-treated filtrate whole yeast treatment step 4
to be introduced.

この酵母処理工程4では、上記濾液を、空気導入により
微好気性に保たれた反応槽内に導入して発酵させる。
In this yeast treatment step 4, the filtrate is introduced into a reaction tank kept microaerobic by introducing air and fermented.

この際、上記濾液のpHが3.0〜8.5の範囲であれ
ばそのまま発酵させる。なお、BOD負荷は3゜OKf
/に9−8S・日以下とし、発酵温度は約15〜25℃
に調整する。そして、運転当初は、5acch&rom
yces属、L)ebaryomyces属、Hans
enula属、Torula属、Pichia属等の酵
母を接種するが、その後は返送による。
At this time, if the pH of the filtrate is in the range of 3.0 to 8.5, it is fermented as is. In addition, the BOD load is 3゜OKf
The fermentation temperature is approximately 15-25℃.
Adjust to. And, at the beginning of operation, 5 ach & rom
yces, L) ebaryomyces, Hans
Yeasts of the genus enula, genus Torula, genus Pichia, etc. are inoculated, but after that, they are returned.

次に、上記酵母処理が終った処理液を遠心分離工程5へ
導入する。
Next, the treated liquid after the yeast treatment is introduced into the centrifugation step 5.

この遠心分離工程4でに、上記処理液が遠心分離機内に
導入されて、濃縮菌体と上澄液とに分離される。
In this centrifugation step 4, the treated liquid is introduced into a centrifugal separator and separated into concentrated bacterial cells and a supernatant.

この際、酵母は粒径が数10μ程度の比較的均一なもの
なので、遠心分離機によって効果的に分離される。そし
て、分離され之濃縮菌体6は含水率が約80〜90%程
度の糊状を呈する。
At this time, since yeast is relatively uniform in particle size of approximately several tens of microns, it can be effectively separated by a centrifuge. The separated and concentrated bacterial cells 6 have a paste-like appearance with a water content of about 80 to 90%.

なお、遠心分離機としては、第2図に示すような、竪形
の遠心分離機11が適している。この竪形の遠心分離機
11は、上記処理液を処理液流入口12から処理液流入
管16全通して回転ポール14内の底部に流入し、回転
ポール14に設けた分離板16に二って濃縮HAと分離
液Bとに分離し、濃縮iAと分離液Bと全回転ポール1
4の上端の濃縮液流出口17及び分離液流出口18から
流出させるようにしたものである。
Note that a vertical centrifuge 11 as shown in FIG. 2 is suitable as the centrifuge. This vertical centrifugal separator 11 allows the processing liquid to flow from the processing liquid inlet 12 through the entire processing liquid inlet pipe 16 into the bottom of the rotary pole 14, and to be separated from the separation plate 16 provided on the rotary pole 14. The concentrated HA and the separated liquid B are separated into the concentrated iA, the separated liquid B and the fully rotating pole 1.
The liquid is allowed to flow out from the concentrated liquid outlet 17 and the separated liquid outlet 18 at the upper end of 4.

なお、上記遠心分離工程で得られた濃縮汚泥は、そのま
ま液肥等として利用する。濃縮菌体6は蛋白質含有率が
60%(40〜70%)程度と高く、ビタミン質も0.
04%(0,03〜0.05%)含有しているため、市
販の酵母エキスとほぼ同等の価値があり、肥料や飼料と
して利用される。
Note that the concentrated sludge obtained in the above centrifugation step is used as it is as liquid fertilizer or the like. Concentrated bacterial cell 6 has a high protein content of about 60% (40-70%) and vitamin content of 0.
Since it contains 0.04% (0.03-0.05%), it has almost the same value as commercially available yeast extract, and is used as fertilizer and feed.

例えば余剰酵母は、キノコ類栽培のための培地に利用す
ると非常に効果がある。
For example, surplus yeast can be very effective when used as a medium for growing mushrooms.

余剰酵母(汚泥)に約10倍量の水全加え、2〜3時間
煮沸し、濾過または静置により上ii’を得る。この上
澄液を酵母エキスとして培地に添加する。この添加iは
蛋白質として培地に対して0゜1〜0.4%程度とする
。また、廃水の成分によっては、余剰酵母を酵母処理工
程から直接採取して、煮沸しても良い。
About 10 times the amount of water is added to the excess yeast (sludge), boiled for 2 to 3 hours, and filtered or left to stand to obtain the above ii'. This supernatant liquid is added to the medium as yeast extract. The amount of protein added to the medium is approximately 0.1 to 0.4%. Further, depending on the components of the wastewater, surplus yeast may be directly collected from the yeast treatment process and boiled.

対象のキノコ類としては、人工栽培可能なエノキダケ、
シメジ、マエタケ、ナメコ、シイタケ。
Target mushrooms include enoki mushrooms, which can be cultivated artificially;
Shimeji, Maetake, Nameko, and Shiitake.

マツシュルーム等カ良イ。Pine mushrooms are nice.

キノコ類は担子菌類(真菌類)に属するので、増殖には
培地が必要である。担子菌類の増殖には、酵母エキス・
ブドウ糖培地、エビオス・ブドウ糖培地、エピオス戸、
糖培地のように、酵母エキスやエビオス(酵母粉末)を
使用している。しかし、これらエキスは非常に高価なた
め、商菓用のキノコ類栽培には使用できず、一般的には
、こぬか等全代りに使用している。
Mushrooms belong to the basidiomycete (fungi) and therefore require a medium for growth. For the growth of basidiomycetes, yeast extract and
Glucose medium, Ebios glucose medium, Epiosto,
Like sugar medium, yeast extract and Ebios (yeast powder) are used. However, these extracts are very expensive and cannot be used to cultivate mushrooms for commercial confectionery, so they are generally used instead of whole mushrooms such as konuka.

しかし、本発明によれば、安価な酵母エキスが得られる
ため、これを培地に使用し、高品質なキノコ類を高収率
で得られる。
However, according to the present invention, since an inexpensive yeast extract can be obtained, it can be used in a culture medium to obtain high-quality mushrooms at a high yield.

一方、上記遠心分離工程で得られた分離液は、接触酸化
処理工程7に導入する。
On the other hand, the separated liquid obtained in the above centrifugation step is introduced into the catalytic oxidation treatment step 7.

この接触酸化処理工程7では、上記分離液が接触酸化処
理槽によって好気性生物処理される。ここでは、ばつ気
は間欠的に行われ、接触酸化処理槽内は嫌気、好気を繰
り返すので、脱窒処理も行われる。
In this contact oxidation treatment step 7, the separated liquid is subjected to aerobic biological treatment in a contact oxidation treatment tank. Here, aeration is performed intermittently, and the inside of the contact oxidation treatment tank repeats anaerobic and aerobic conditions, so that denitrification treatment is also performed.

また、接触酸化処理槽内には通常の場合と同様に、波板
等の接触ろ材が充填され、ばつ気により槽内に循環流が
生起される。なお、嫌気工程はばつ気全停止しても、他
の攪拌装置で攪拌?行っても、或いはばつ気の空気量全
滅らしても良い。また、接触酸化処理にかえて、通常の
活性汚泥処理全採用してもよい。
Further, the contact oxidation treatment tank is filled with a contact filter material such as a corrugated plate, as in the usual case, and a circulating flow is generated in the tank by aeration. In addition, even if the anaerobic process is completely stopped, is it still possible to stir it with another stirring device? You can go there, or you can run out of air. Further, instead of the catalytic oxidation treatment, all normal activated sludge treatment may be employed.

最後に、上記接触酸化処理が終つ友処理液金、沈殿処理
後、滅菌処理工程8へ導入する。
Finally, the liquid gold treated after the catalytic oxidation treatment is introduced into the sterilization treatment step 8 after the precipitation treatment.

この滅菌処理工程8では、上記処理液全塩素消毒槽内に
導入して、注入される塩素によって消毒する。
In this sterilization treatment step 8, the treatment solution is introduced into the total chlorination tank and disinfected by the injected chlorine.

なお、処理液の残留塩素が1〜/1以上となるように、
通常的15jψ−cl/l程度の塩素を注入する。
In addition, so that the residual chlorine of the treatment liquid is 1 to 1 or more,
Typically, chlorine is injected at a rate of about 15jψ-cl/l.

そして、上記滅菌処理が終った滅菌処理液9の一部は、
前記酵母処理工程4へ返送される。酵母は細菌に比べて
塩素等酸化剤に対する耐性が強いので、上記返送により
発酵時の一般細菌の増殖が抑えられる。
A part of the sterilized liquid 9 after the sterilization process is
The yeast is returned to the yeast treatment step 4. Since yeast is more resistant to oxidizing agents such as chlorine than bacteria, the above-mentioned return suppresses the growth of general bacteria during fermentation.

なお、次表は、本発明の実施例を示したものであり、廃
水処理量1.000m’/日から、濃縮菌体450 K
?−乾物7日(含水率80〜90%)が得られた。
The following table shows examples of the present invention, and from a wastewater treatment amount of 1.000 m'/day, concentrated bacterial cells of 450 K
? - 7 days dry matter (moisture content 80-90%) was obtained.

また、蛋白質含有率60%(40〜70%)、ビタミン
質含有率0.04%であった。
Further, the protein content was 60% (40-70%) and the vitamin content was 0.04%.

以上、本発明の実施例に付き述べたが、本発明の技術的
思想に基づいて各種の有効な変更が可能である。
Although the embodiments of the present invention have been described above, various effective modifications can be made based on the technical idea of the present invention.

例えば、対象とする廃水は、高11度廃水が最適であり
、製パン廃水(糖、でんぷん)、製菓廃水(でんぷん、
オリブ塘、ペクチン)、ハム製造廃水(油脂、蛋白質)
等の食品工場廃水の他、ホテル、厨房廃水(油脂)、し
尿や家畜糞尿等を用いることができる。
For example, the optimal target wastewater is high-11 degree wastewater, breadmaking wastewater (sugar, starch), confectionery wastewater (starch,
olive tang, pectin), ham manufacturing wastewater (oil, fat, protein)
In addition to food factory wastewater such as , hotel and kitchen wastewater (oil and fat), human waste, livestock manure, etc. can be used.

また、酵母処理に関しては、酵母を浮遊させる方法でも
、坦体に固定する方法でも良い。坦体としては、そのま
ま飼料、肥料になると共に、安定であるゼオライト、ソ
フトセラミックス、珪藻土、等が好ましい。
Further, regarding the yeast treatment, a method in which the yeast is suspended or a method in which the yeast is immobilized on a carrier may be used. As the carrier, zeolite, soft ceramics, diatomaceous earth, etc., which can be used directly as feed or fertilizer and are stable, are preferable.

また、廃水の種類によって使用酵母を決定し、馴養時に
、は、これら酵母?別途培養して添加するのが好ましい
Also, determine the yeast to be used depending on the type of wastewater, and during acclimatization, are these yeasts? It is preferable to culture it separately and add it.

即ち、し尿、家畜糞尿に対しては、(、:andida
属、Saccharomyces属が、糖質廃液(製パ
ン、製菓)に対しては、Saccharomeces属
、Debaryomyces属、HansenuAa属
、’L’orula属、Pichia属が、油脂廃i(
ホテル、厨房廃液)に対しては、Candida属、L
Jebaryomyces属の酵母が好ましい。
That is, for human waste and livestock manure, (,:andida
The genus Saccharomyces, the genus Debaryomyces, the genus HansenuAa, the genus 'L'orula, and the genus Pichia are used for sugar waste liquid (bread making, confectionery), and the genus Saccharomyces, the genus Debaryomyces, the genus 'L'orula, and the genus Pichia,
For hotels, kitchen waste), Candida spp., L.
Yeasts of the genus Jebaryomyces are preferred.

また、濃縮画体を液肥として利用する場合は、坦体を添
加せず、浮遊法とするのが好ましい。
Further, when the concentrated image is used as liquid fertilizer, it is preferable to use a floating method without adding a carrier.

また、酵母処理液からの菌体の分離は、遠心分離の他、
膜や重力濃縮等であっても良い。
In addition to centrifugation, bacterial cells can be separated from the yeast treatment solution by
A membrane, gravity concentration, etc. may also be used.

また、1!に縮菌体全飼料とする場合、ぬか、おから、
脱脂大豆、ゼオライト等を添加し、水分調整全行うのが
好ましい。また、肥料化の場合は、ゼオライト、珪藻土
、腐殖土、ピートモス等を添加するのが好ましい。また
、これら最終製品は必要に応じてペレット化すると艮い
Also, 1! When using whole condensed bacteria as feed, bran, okara,
It is preferable to add defatted soybeans, zeolite, etc. to completely adjust the moisture content. In the case of fertilizer, it is preferable to add zeolite, diatomaceous earth, humus, peat moss, etc. In addition, these final products can be pelletized if necessary.

〔発明の効果〕〔Effect of the invention〕

本発明の廃水による酵母の培養方法によれば、廃水中の
固形有機物の多くは可溶化消化処理によって液化される
ために、菌体の回収量が多くなる。
According to the method for culturing yeast using wastewater of the present invention, most of the solid organic matter in the wastewater is liquefied by the solubilization and digestion treatment, so that a large amount of bacterial cells can be recovered.

しかも、可溶化消化によっても液化できなかった固形物
に、スクリーン処理によって除去される次めに、酵母処
理によって得られる菌体の純度が高第 くなり、蛋白質の含有率が高く、飼料、肥料として商品
価値が高い。
In addition, the solids that could not be liquefied by solubilization digestion are removed by screen treatment, and the bacteria obtained by yeast treatment have a high purity and a high protein content, and can be used as feed, fertilizer, etc. It has a high commercial value.

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

′$J1図は本発明の工程11貞?説明するブロック図
、第2図は遠心分離機の一例を示した概略図である。 1・・・廃水、2・・・可溶化消化処理工程、6・・・
スクリーン処理工程、4・・・酵母処理工程、6.・・
濃縮菌体。 特許出願人  株式会社西原環境衛生研究所特許出願人
 日本微生物化学株式会社 1図
'Is the $J1 diagram the process 11 of the present invention? The block diagram to be described, FIG. 2, is a schematic diagram showing an example of a centrifugal separator. 1... Wastewater, 2... Solubilization and digestion process, 6...
Screen treatment step, 4... Yeast treatment step, 6.・・・
Concentrated bacterial cells. Patent applicant Nishihara Environmental Health Research Institute Co., Ltd. Patent applicant Nippon Microbial Chemistry Co., Ltd. Figure 1

Claims (1)

【特許請求の範囲】[Claims] 廃水を所定期間嫌気状態に保持して可溶化消化し、その
処理液をスクリーンで濾過してし渣を除去し、その濾液
を酵母処理して酵母を回収するようにした廃水による酵
母の培養方法。
A method for culturing yeast using wastewater, in which wastewater is maintained in an anaerobic state for a predetermined period of time for solubilization and digestion, the treated liquid is filtered through a screen to remove residue, and the filtrate is treated with yeast to recover yeast. .
JP61080985A 1986-04-10 1986-04-10 Cultivation of yeast with waste water Granted JPS62239983A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61080985A JPS62239983A (en) 1986-04-10 1986-04-10 Cultivation of yeast with waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61080985A JPS62239983A (en) 1986-04-10 1986-04-10 Cultivation of yeast with waste water

Publications (2)

Publication Number Publication Date
JPS62239983A true JPS62239983A (en) 1987-10-20
JPH044867B2 JPH044867B2 (en) 1992-01-29

Family

ID=13733791

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61080985A Granted JPS62239983A (en) 1986-04-10 1986-04-10 Cultivation of yeast with waste water

Country Status (1)

Country Link
JP (1) JPS62239983A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH01293194A (en) * 1988-05-18 1989-11-27 Yuukishitsu Hiryo Seibutsu Katsusei Riyou Gijutsu Kenkyu Kumiai High load treatment of carbohydrate waste water

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS57152887A (en) * 1981-03-18 1982-09-21 Nitto Electric Ind Co Ltd Treatment of liquid
JPS59115795A (en) * 1982-12-24 1984-07-04 Sanyo Kokusaku Pulp Co Ltd Treatment of waste liquid of pulp digester
JPS6029678A (en) * 1983-07-28 1985-02-15 Fujitsu Ltd Gate injecting current measuring device of mosfet

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS57152887A (en) * 1981-03-18 1982-09-21 Nitto Electric Ind Co Ltd Treatment of liquid
JPS59115795A (en) * 1982-12-24 1984-07-04 Sanyo Kokusaku Pulp Co Ltd Treatment of waste liquid of pulp digester
JPS6029678A (en) * 1983-07-28 1985-02-15 Fujitsu Ltd Gate injecting current measuring device of mosfet

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH01293194A (en) * 1988-05-18 1989-11-27 Yuukishitsu Hiryo Seibutsu Katsusei Riyou Gijutsu Kenkyu Kumiai High load treatment of carbohydrate waste water
JPH0466639B2 (en) * 1988-05-18 1992-10-23 Jukishitsu Hiryo Seibutsu Katsusei Ryo Gijutsu Kenkyu Kumiai

Also Published As

Publication number Publication date
JPH044867B2 (en) 1992-01-29

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