JPH10118680A - Method and apparatus for wastewater treatment material production - Google Patents
Method and apparatus for wastewater treatment material productionInfo
- Publication number
- JPH10118680A JPH10118680A JP27957496A JP27957496A JPH10118680A JP H10118680 A JPH10118680 A JP H10118680A JP 27957496 A JP27957496 A JP 27957496A JP 27957496 A JP27957496 A JP 27957496A JP H10118680 A JPH10118680 A JP H10118680A
- Authority
- JP
- Japan
- Prior art keywords
- mixture
- treatment material
- decomposed
- fermented
- charcoal
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Biological Treatment Of Waste Water (AREA)
Abstract
Description
【０００１】[0001]
【発明の属する技術分野】本発明は培養基としての茸栽
培後の廃床の再利用により汚水や排水の浄水化を図る汚
水処理材の製造方法及びその装置に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for manufacturing a sewage treatment material for purifying sewage and wastewater by reusing a waste floor after mushroom cultivation as a culture medium.
【０００２】[0002]
【従来の技術】この種の茸栽培においては、オガクズを
主体とする培養基を用いるオガクズ栽培が採用され、栽
培後において、廃床として廃棄処理されるが、近年の茸
栽培の需要の増大化により、大量の廃床が廃棄処理され
ている。この廃床の組成としては、オガクズ、米ヌカ、
コーンブラン（トウモロコシの芯）、キノコクズ、菌糸
体などからなる。ここにオガクズは成分がリグニン、繊
維組（セルロース）で分解処理が難しい性質をもち、他
の組成は全部タンパク源で分解が容易であり、但し、タ
ンパク源は腐敗し易いので管理面で注意を要するとされ
る。2. Description of the Related Art In this type of mushroom cultivation, sawdust cultivation using a culture medium mainly composed of sawdust is employed, and after cultivation, it is discarded as a waste floor. A large amount of waste floors are being disposed of. The composition of this waste floor includes sawdust, rice bran,
It consists of corn bran (corn core), mushrooms and mycelium. Sawdust contains lignin and fiber (cellulose), which are difficult to decompose, and all other components are easily decomposed by protein sources. However, protein sources are easily decomposed, so care must be taken in terms of management. It is required.
【０００３】ところで、近年にあって、漸く、このよう
に大量に廃棄される廃床を再利用する方法が検討されて
いる。例えば、廃床を産業廃棄物として一年乃至二年程
度の期間を掛けて野積して自然風化させ、この風化した
廃床の一部を、畑地において、肥料として使用したり、
焼却廃棄処理したり、燃料として用いたり、牛糞と混ぜ
て、一部堆肥として用いたりしている。[0003] In recent years, a method of reusing such a large amount of discarded waste floor is being studied. For example, over a period of about one to two years, waste floors are used as industrial waste for natural accumulation and natural weathering, and a part of this weathered waste floor is used as fertilizer in upland fields,
They are incinerated, used as fuel, or mixed with cow dung to be partially used as compost.
【０００４】[0004]
【発明が解決しようとする課題】しかしながらこのよう
に処理された廃床にあっては、酸性度が高いためにすぐ
に肥料として使用できないことがあり、又、リグニン質
が生動植物に悪影響を与える恐れもあり、従って、処理
難及び用途難により再利用が困難となっているという不
都合を有している。However, the waste floor treated in this way cannot be used immediately as fertilizer due to high acidity, and lignin has a bad influence on living plants and animals. There is also a disadvantage that it is difficult to recycle due to difficulties in processing and use.
【０００５】[0005]
【課題を解決するための手段】本発明はこのような不都
合を解決することを目的とするもので、本発明のうち
で、請求項１記載の汚水処理材の製造方法の発明は、茸
の菌糸体を含む廃床と木炭と少なくとも乳酸菌及び酵母
菌からなる微生物と水とを所定割合をもって混合撹拌さ
せると共に該混合物を所定時間の撹拌により生ずる発熱
によって醗酵及び分解させ、該醗酵分解した混合物を袋
詰して所定日数放置して熟成させ、該熟成した混合物を
乾燥させることを特徴とするものである。An object of the present invention is to solve such inconvenience. Among the present invention, the invention of the method for producing a sewage treatment material according to the first aspect of the present invention is directed to mushrooms. The waste bed containing mycelium, charcoal, at least a microorganism composed of at least lactic acid bacteria and yeast and water are mixed and stirred at a predetermined ratio, and the mixture is fermented and decomposed by heat generated by stirring for a predetermined time. The bag is packed and left for a predetermined number of days for aging, and the aged mixture is dried.
【０００６】又、請求項２記載の発明は、上記混合物に
微生物としての光合成菌を添加してなることを特徴とす
るものであり、又、請求項３記載の発明は、上記混合物
に籾の燻炭を添加してなることを特徴とするものであ
り、又、請求項４記載の発明は、上記木炭として粉炭を
用いてなることを特徴とするものである。[0006] The invention according to claim 2 is characterized in that photosynthetic bacteria as microorganisms are added to the mixture, and the invention according to claim 3 is characterized in that rice hulls are added to the mixture. The present invention is characterized in that charcoal is added, and the invention according to claim 4 is characterized in that pulverized coal is used as the charcoal.
【０００７】又、請求項５記載の汚水処理材の製造装置
にあっては、茸の菌糸体を含む廃床と木炭と少なくとも
乳酸菌及び酵母菌からなる微生物と水とを所定割合をも
って混合撹拌させると共に該混合物を所定時間の撹拌に
より生ずる発熱によって醗酵及び分解させる撹拌醗酵部
と、該醗酵分解した混合物を袋詰する袋詰部と、該袋詰
めされた混合物をそのまま所定日数放置して熟成させる
熟成部と、該熟成した混合物を乾燥させる乾燥部とを備
えてなることを特徴とするものである。According to a fifth aspect of the present invention, there is provided an apparatus for producing a sewage treatment material, wherein a waste floor containing mycelia of mushrooms, charcoal, microorganisms comprising at least lactic acid bacteria and yeast and water are mixed and stirred at a predetermined ratio. At the same time, a stirred fermentation unit for fermenting and decomposing the mixture by heat generated by stirring for a predetermined time, a bagging unit for bagging the fermented and decomposed mixture, and allowing the bagged mixture to stand for a predetermined number of days to mature. It is characterized by comprising an aging part and a drying part for drying the aged mixture.
【０００８】[0008]
【発明の実施の形態】図１乃至図４は本発明の実施の形
態例を示し、図１は製造工程図、図２は製造装置の構成
系統図である。1 to 4 show an embodiment of the present invention. FIG. 1 is a manufacturing process diagram, and FIG. 2 is a structural system diagram of a manufacturing apparatus.
【０００９】図１及び図２において、先ず、茸栽培の結
果生ずる栽培基としての茸の菌糸体を含む廃床と、粉炭
とした木炭と、少なくとも乳酸菌及び酵母菌からなる微
生物と、水とを所定割合、例えば、廃床１００ｇと、木
炭０．５ｇと、少なくとも液体としての乳酸菌及び酵母
菌からなる微生物０．１ｇと、水３０ｇとをもって混合
撹拌させ、更に具体的には微生物として、乳酸菌：酵母
菌：必要に応じて光合成菌＝３：１：１の割合とし、
又、必要に応じて、籾の燻炭を０．３ｇ程度添加し、こ
の混合物を所定時間、例えば二四時間（約１日）程度撹
拌し、撹拌により生ずる摩擦や動力熱による自然発熱に
よって混合物を醗酵及び分解させる。In FIG. 1 and FIG. 2, first, a waste floor containing mushroom mycelium as a cultivation base resulting from mushroom cultivation, charcoal made into powdered charcoal, a microorganism comprising at least lactic acid bacteria and yeast, and water are mixed. A predetermined ratio, for example, 100 g of waste floor, 0.5 g of charcoal, 0.1 g of a microorganism composed of at least lactic acid bacteria and yeast as a liquid, and 30 g of water are mixed and stirred. Yeast: photosynthetic bacterium = 3: 1: 1 ratio as required,
Also, if necessary, about 0.3 g of charcoal of the paddy is added, and the mixture is stirred for a predetermined time, for example, about 24 hours (about 1 day), and the mixture is generated by friction generated by the stirring and spontaneous heat generation due to power heat. Is fermented and decomposed.
【００１０】この場合、撹拌醗酵部Ｈは、図３、図４に
示すような撹拌機１により撹拌し、この撹拌機１は容器
体２内に回転軸３を架設し、回転軸３に複数個の撹拌羽
根４を突設し、回転軸３をモータ５により回転させ、複
数個の回転羽根４によって混合物を撹拌させる構造とな
っている。In this case, the stirred fermentation section H is stirred by a stirrer 1 as shown in FIGS. 3 and 4, and this stirrer 1 has a rotating shaft 3 installed in a container body 2 and a plurality of rotating shafts 3 A plurality of stirring blades 4 protrude, the rotating shaft 3 is rotated by a motor 5, and the mixture is stirred by the plurality of rotating blades 4.
【００１１】次いで、この撹拌混合による発熱によって
醗酵、分解された混合物Ｗを容器体２内から取出口６を
介して計量して取出し、具体的には醗酵度合いは７０％
程度となっており、合成樹脂製の袋等により袋詰部Ｆに
より袋詰し、熟成部Ｋにおいて、その袋のまま、所定日
数、例えば２０日間程度、常温で放置して熟成させ、具
体的には醗酵度合いを８０〜９０％程度とする。Next, the mixture W fermented and decomposed by the heat generated by the stirring and mixing is weighed out of the container 2 through the outlet 6, and specifically, the fermentation degree is 70%.
The bag is filled with a bag made of a synthetic resin or the like in a bag-filling section F. In the ripening section K, the bag is aged for a predetermined number of days, for example, about 20 days at room temperature, and aged. The fermentation degree is set to about 80 to 90%.
【００１２】そして、この熟成した混合物を乾燥部Ｍに
おいて、自然乾燥又は強制乾燥により乾燥させることに
より汚水処理材を製造することになる。Then, the aged mixture is dried in the drying section M by natural drying or forced drying to produce a sewage treatment material.
【００１３】この際、例えば時間を置かずに直ちに汚水
処理材として使用する場合には水分含有率が４５％程度
の生乾燥状態とし、又、長期間経過後において、使用さ
れるような場合には、水分含有率が１５％程度となる乾
燥状態とし、経年変化に対応できるようにする。At this time, for example, when the material is used immediately as a sewage treatment material without leaving a time, the moisture content is made to be a freshly dried state having a water content of about 45%. Is a dry state having a water content of about 15% so that it can cope with aging.
【００１４】この実施の形態例においては、茸の菌糸体
を含む廃床と木炭と少なくとも乳酸菌及び酵母菌からな
る微生物と水とを所定割合をもって混合撹拌させると共
に該混合物を所定時間の撹拌により生ずる発熱によって
醗酵及び分解させ、該醗酵分解した混合物を袋詰して所
定日数放置して熟成させ、該熟成した混合物を乾燥させ
て製造され、この汚水処理材を袋から取り出して水中に
散布したり、又は、網袋や穴付き袋などに入れて水中に
投入したり、又は圧縮成型してペレット状の固形物とし
て水中に投入して使用することになり、この汚水処理材
は、物の腐敗及び鉄を錆びさせないという抗酸化力を持
つと共に腐敗の進行を止めて元の有機物に復元させる汚
物の高復元力を併せ持つので、少量でも、大量の汚水、
排水浄化能力を持ち、貯水池などに使用する貯水型使用
並びに流水型使用にあっても共通となる利便性があっ
て、使用の融通性を高めることができ、又、リサイクル
性、経済性、安価及び供給安定性も高く、環境性、自然
循環型リサイクル性も高いと共に鉄さび防止力が強く、
更には２０℃〜３０℃帯程度の低温発酵分解能力が優れ
ているので、化学変化を用いた場合のように７０℃〜９
０℃程度の高温度を必要とせずに熟成させることがで
き、一層容易にかつ低廉に製造することができる。In this embodiment, a waste floor containing mycelium of mushrooms, charcoal, a microorganism comprising at least lactic acid bacteria and yeast and water are mixed and stirred at a predetermined ratio, and the mixture is formed by stirring for a predetermined time. The mixture is fermented and decomposed by heat generation, and the fermented and decomposed mixture is packed in a bag, left to age for a predetermined number of days, aged, dried and manufactured, and this sewage treatment material is taken out of the bag and sprayed into water. Or put in water in a net bag or a bag with holes, or put it into water by compression molding and put it in water as a pellet-like solid. And it has the antioxidant power that does not rust iron and has the high resilience of filth that stops the progress of decay and restores to the original organic matter, so even a small amount, a large amount of sewage,
It has the ability to purify wastewater, and has the same convenience for both storage type and running water type used in reservoirs, etc., which can increase the flexibility of use, and is also recyclable, economical and inexpensive. It also has high supply stability, environmentally friendly, natural recycling type recyclability and strong iron rust prevention,
Furthermore, since the low-temperature fermentation decomposition ability in the range of about 20 ° C. to 30 ° C. is excellent, it is possible to use 70 ° C. to 9 ° C.
The aging can be performed without requiring a high temperature of about 0 ° C., and the production can be performed more easily and at low cost.
【００１５】具体的な実施例として、茸工場から排水さ
れる汚水の貯水槽に使用した結果は次のとおりであっ
た。[0015] As a specific example, the results of using the wastewater drainage tank drained from a mushroom factory as follows.
【００１６】この貯水槽の大きさは、縦４０ｍ×横３ｍ
×水深２５ｃｍの水槽が二槽からなり、水量としては約
５０ｔｏｎであり、水温は２５℃〜４０℃、平均水温は
約３０℃であり、最初は本汚水処理材を１５Ｋｇ入りの
網袋を三個合計４５Ｋｇ投入して一ケ月間放置し、次に
１５Ｋｇ入りの網袋を二個合計３０Ｋｇ投入して二ケ月
間放置し、次いで、１５Ｋｇ入りの網袋を一個１５Ｋｇ
投入して一ケ月間放置した。The size of this water storage tank is 40 m long × 3 m wide.
× A water tank with a depth of 25 cm is composed of two tanks, the amount of water is about 50 tons, the water temperature is 25 ° C to 40 ° C, the average water temperature is about 30 ° C, and at first, a net bag containing 15 kg of the wastewater treatment material is used. Put a total of 45 kg and leave it for one month, then put two net bags containing 15 kg and leave it for two months and put in a total of 30 kg, then put a 15 kg net bag with 15 kg.
It was put in and left for one month.
【００１７】この結果、汚水処理材を合計９０Ｋｇ投入
したことになり、５０ｋｇを投入した時点としての開始
から１〜２カ月後においては、汚水は浄化して活水化
し、当初のＰＨ値が５〜６程度であったのが７〜８の中
性に保たれ、臭気も当初、最悪の臭気度４であったの
が、臭気度１程度の無臭状態となり、更には、生物の発
生、モノアラガイ、サカマキガイ、メダカ、ヤゴ、ほた
る、他の小生物の発生及び増殖もみられる程に浄化し、
しかも鉄さびを取る効果も発揮され、分解された汚物、
タンパク源をえさとして微生物が繁殖活動することも分
り、逆に水を腐敗型とするアオミドロや藻類等の消失も
見られ、又、使用後の本汚水処理材の残留物は土に帰る
同化性が高く、化学薬品等と違い、副作用や公害性もな
いことが分った。As a result, a total of 90 kg of the sewage treatment material was charged, and one to two months after the start when 50 kg was charged, the sewage was purified and activated, and the initial PH value was 5 to 5. About 6 was maintained at 7 to 8 neutrality, and the odor was initially the worst odor of 4, but it became an odorless state with about 1 odor. Purify so that the generation and proliferation of oyster oysters, medaka, yago, fireflies, and other small organisms can be seen,
In addition, the effect of removing iron rust is also exhibited,
It is also known that microorganisms propagate by using the protein source as feed.On the contrary, there are disappearance of spoilage and algae that make water decay, and the residue of this wastewater treatment material after use is returned to soil. High, and unlike chemicals, there were no side effects or pollution.
【００１８】又、生物学見地からの評価によれば、貝、
めだか、ほたる、等生息体が繁殖、生息する状態は理想
的な自然環境であり、好ましいという評価となった。According to the evaluation from a biological point of view,
The state where medaka, firefly, etc. inhabit and breed and inhabit is an ideal natural environment, and was evaluated as favorable.
【００１９】従って、自然環境リサイクル型、産業廃棄
物の再利用処理材の開発となり、廃床中に残っている菌
糸体と微生物とによりなされる抗酸化発酵分解能力を利
用するからであり、そして、廃床の悪性であるリグニン
と繊維組（セルロース）の分解難を例えば一日程度の短
時間で回転加圧撹拌熱処理法で用途性の拡大を可能にし
たものであるといえる。Therefore, a natural environment recycling type industrial waste recycle material is developed, and the antioxidative fermentative decomposition ability of the mycelium and the microorganisms remaining in the waste floor is utilized. It can be said that the difficulty in decomposing the lignin and the fiber group (cellulose), which are the malignant substances in the waste floor, can be expanded by the rotary pressure stirring heat treatment method in a short time, for example, about one day.
【００２０】又、この場合、上記混合物に微生物として
の光合成菌を添加してなるから、例えばマイタケ栽培後
の廃床においては分解能力を促進して浄水能力が高めら
れ、又、この場合上記混合物に籾の燻炭を添加してなる
から、多孔質故に醗酵ガスを良好に消去すると共に微生
物のすみかともなり、それだけ浄水能力を高めることが
でき、又、この場合、上記木炭として粉炭を用いてなる
から、同様に多孔質故に醗酵ガスを良好に消去すると共
に微生物のすみかともなり、それだけ水の浄化を促進す
ることができる。In this case, since photosynthetic bacteria as microorganisms are added to the mixture, for example, in a waste floor after cultivation of maitake, the decomposition ability is promoted to increase the water purification ability. Since the charcoal of the paddy is added, the fermentation gas can be satisfactorily eliminated because of the porosity, and it also becomes a home for microorganisms, so that the water purification capacity can be increased accordingly.In this case, pulverized coal is used as the charcoal. Therefore, the fermentation gas can be satisfactorily eliminated because of the porosity, and at the same time, it becomes a home for microorganisms.
【００２１】尚、本発明は上記実施の形態例に限られる
ものではなく、撹拌醗酵部Ｈ、袋詰部Ｆ、熟成部Ｋ及び
乾燥部Ｍの構造等は適宜変更して設計されるものであ
る。The present invention is not limited to the above embodiment, and the structures of the stirred fermentation section H, the bagging section F, the aging section K, and the drying section M are designed by appropriately changing. is there.
【００２２】[0022]
【発明の効果】本発明は上述の如く、請求項１又は５記
載の発明にあっては、茸の菌糸体を含む廃床と木炭と少
なくとも乳酸菌及び酵母菌からなる微生物と水とを所定
割合をもって混合撹拌させると共に該混合物を所定時間
の撹拌により生ずる発熱によって醗酵及び分解させ、該
醗酵分解した混合物を袋詰して所定日数放置して熟成さ
せ、該熟成した混合物を乾燥させて製造され、この汚水
処理材を袋から取り出して水中に散布したり、又は、網
袋や穴付き袋などに入れて、水中に投入して使用投入し
たり、又は圧縮成型してペレット状の固形物として水中
に投入して使用することになり、この汚水処理材は、物
の腐敗及び鉄を錆びさせないという抗酸化力を持つと共
に腐敗の進行を止めて元の有機物に復元させる汚物の高
復元力を併せ持つので、少量でも、大量の汚水、排水浄
化能力を持ち、貯水池などに使用する貯水型使用並びに
流水型使用にあっても共通となる利便性があって、使用
の融通性を高めることができ、又、リサイクル性、経済
性、安価及び供給安定性も高く、環境性、自然循環型リ
サイクル性も高いと共に鉄さび防止力が強く、更には２
０℃〜３０℃帯程度の低温発酵分解能力が優れているの
で、化学変化を用いた場合のように７０℃〜９０℃程度
の高温度を必要とせずに熟成させることができ、一層容
易にかつ低廉に製造することができる。According to the present invention, as described above, in the invention according to claim 1 or 5, the waste floor containing the fungal mycelia of mushrooms, charcoal, a microorganism comprising at least lactic acid bacteria and yeast and water at a predetermined ratio. The mixture is stirred and mixed, and the mixture is fermented and decomposed by heat generated by stirring for a predetermined time.The fermented and decomposed mixture is bagged, left to stand for a predetermined number of days, aged, and the aged mixture is dried to produce a mixture. Take this sewage treatment material out of the bag and spray it in water, or put it in a mesh bag or a bag with holes, put it in water and use it, or compress it and mold it in water as a pellet-like solid. This sewage treatment material has the antioxidant power of preventing the decay of the material and the rusting of iron, and also has the high resilience of the filth to stop the progress of the rot and restore the original organic matter. Even in small quantities, it has a large amount of sewage and drainage purification capacity, and it has the same convenience even for storage type use and running water type use for reservoirs, etc., and can increase the flexibility of use, In addition, it has high recyclability, economic efficiency, low cost, and stable supply. It also has high environmental and natural recycling recyclability and strong iron rust prevention.
Since the low-temperature fermentation decomposition ability in the range of 0 ° C to 30 ° C is excellent, aging can be performed without requiring a high temperature of about 70 ° C to 90 ° C as in the case of using a chemical change. And it can be manufactured at low cost.
【００２３】又、請求項２記載の発明にあっては、上記
混合物に微生物としての光合成菌を添加してなるから、
例えばマイタケ栽培後の廃床においては分解能力を促進
して浄水能力が高められ、又、請求項３記載の発明にあ
っては、上記混合物に籾の燻炭を添加してなるから、多
孔質故に醗酵ガスを良好に消去すると共に微生物のすみ
かともなり、それだけ浄水能力を高めることができ、
又、請求項４記載の発明にあっては、上記木炭として粉
炭を用いてなるから、同様に多孔質故に醗酵ガスを良好
に消去すると共に微生物のすみかともなり、それだけ水
の浄化を促進することができる。According to the second aspect of the present invention, a photosynthetic bacterium as a microorganism is added to the mixture.
For example, in the waste floor after cultivation of maitake, the water purification capacity is enhanced by promoting the decomposition ability. In the invention according to claim 3, since the charcoal of the paddy is added to the mixture, it is porous. Therefore, fermentation gas can be eliminated well and it also becomes a home for microorganisms.
Further, in the invention according to claim 4, since powdered charcoal is used as the charcoal, the fermentation gas is similarly favorably eliminated because of the porous nature, and also serves as a home for microorganisms. Can be.
【００２４】以上初期の目的を充分達成することができ
る。As described above, the initial object can be sufficiently achieved.
【図１】本発明の実施の形態例の製造工程図である。FIG. 1 is a manufacturing process diagram of an embodiment of the present invention.
【図２】本発明の実施の形態例の製造装置の構成系統図
である。FIG. 2 is a configuration system diagram of a manufacturing apparatus according to an embodiment of the present invention.
【図３】本発明の実施の形態例の撹拌機の全体側面図で
ある。FIG. 3 is an overall side view of the stirrer according to the embodiment of the present invention.
【図４】本発明の実施の形態例の撹拌機の横断面図であ
る。FIG. 4 is a cross-sectional view of the stirrer according to the embodiment of the present invention.
Ｈ 撹拌醗酵部 Ｆ 袋詰部 Ｋ 熟成部 Ｍ 乾燥部 H Stirred fermentation section F Bagging section K Aging section M Drying section
Claims (5)
も乳酸菌及び酵母菌からなる微生物と水とを所定割合を
もって混合撹拌させると共に該混合物を所定時間の撹拌
により生ずる発熱によって醗酵及び分解させ、該醗酵分
解した混合物を袋詰して所定日数放置して熟成させ、該
熟成した混合物を乾燥させることを特徴とする汚水処理
材の製造方法。1. A waste bed containing mycelium of mushrooms, charcoal, a microorganism comprising at least lactic acid bacteria and yeast and water are mixed and stirred at a predetermined ratio, and the mixture is fermented and decomposed by heat generated by stirring for a predetermined time. A method for producing a sewage treatment material, wherein the fermented and decomposed mixture is bagged, left to stand for a predetermined number of days to age, and the aged mixture is dried.
添加してなる汚水処理材の製造方法。2. A method for producing a sewage treatment material comprising adding a photosynthetic bacterium as a microorganism to the mixture.
水処理材の製造方法。3. A method for producing a sewage treatment material comprising adding charcoal of paddy to the mixture.
理材の製造方法。4. A method for producing a sewage treatment material using pulverized coal as the charcoal.
も乳酸菌及び酵母菌からなる微生物と水とを所定割合を
もって混合撹拌させると共に該混合物を所定時間の撹拌
により生ずる発熱によって醗酵及び分解させる撹拌醗酵
部と、該醗酵分解した混合物を袋詰する袋詰部と、該袋
詰めされた混合物をそのまま所定日数放置して熟成させ
る熟成部と、該熟成した混合物を乾燥させる乾燥部とを
備えてなる汚水処理材の製造装置。5. A waste bed containing mycelium of mushrooms, charcoal, microorganisms consisting of at least lactic acid bacteria and yeast and water are mixed and stirred at a predetermined ratio, and the mixture is fermented and decomposed by heat generated by stirring for a predetermined time. A stirring fermentation unit, a bagging unit for bagging the fermented and decomposed mixture, an aging unit for allowing the bagged mixture to stand for a predetermined number of days, and a drying unit for drying the aged mixture. Sewage treatment material manufacturing equipment.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP27957496A JPH10118680A (en) | 1996-10-22 | 1996-10-22 | Method and apparatus for wastewater treatment material production |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP27957496A JPH10118680A (en) | 1996-10-22 | 1996-10-22 | Method and apparatus for wastewater treatment material production |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH10118680A true JPH10118680A (en) | 1998-05-12 |
Family
ID=17612886
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP27957496A Pending JPH10118680A (en) | 1996-10-22 | 1996-10-22 | Method and apparatus for wastewater treatment material production |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH10118680A (en) |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6841180B2 (en) * | 2001-05-07 | 2005-01-11 | Biohub Co., Ltd. | Method for preparing lactic acid fermented solution of mushroom and lactic acid fermented solution of mushroom produced thereby |
| JP2007260549A (en) * | 2006-03-28 | 2007-10-11 | Dowa Holdings Co Ltd | Water cleaning method and apparatus |
| CN100355665C (en) * | 2005-01-28 | 2007-12-19 | 湖南大学 | Method of adsorbing lead-contained in industial wste water using mushroom culture medium waste material |
| CN100355664C (en) * | 2005-01-28 | 2007-12-19 | 湖南大学 | Method for adsorbing chromium-contained in industrial waste water using mushroom culture medium waste material |
| JP2010221213A (en) * | 2009-02-27 | 2010-10-07 | Keisuke Takenouchi | Water treatment technique using filamentous fungus or actinomycete |
| JP2018121582A (en) * | 2017-02-01 | 2018-08-09 | ルーテック株式会社 | Method for inhibiting growth of filamentous algae that coexist with water-immersed plants |
-
1996
- 1996-10-22 JP JP27957496A patent/JPH10118680A/en active Pending
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6841180B2 (en) * | 2001-05-07 | 2005-01-11 | Biohub Co., Ltd. | Method for preparing lactic acid fermented solution of mushroom and lactic acid fermented solution of mushroom produced thereby |
| CN100355665C (en) * | 2005-01-28 | 2007-12-19 | 湖南大学 | Method of adsorbing lead-contained in industial wste water using mushroom culture medium waste material |
| CN100355664C (en) * | 2005-01-28 | 2007-12-19 | 湖南大学 | Method for adsorbing chromium-contained in industrial waste water using mushroom culture medium waste material |
| JP2007260549A (en) * | 2006-03-28 | 2007-10-11 | Dowa Holdings Co Ltd | Water cleaning method and apparatus |
| JP2010221213A (en) * | 2009-02-27 | 2010-10-07 | Keisuke Takenouchi | Water treatment technique using filamentous fungus or actinomycete |
| JP2018121582A (en) * | 2017-02-01 | 2018-08-09 | ルーテック株式会社 | Method for inhibiting growth of filamentous algae that coexist with water-immersed plants |
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