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JPH0742185B2 - Compost manufacturing method and device - Google Patents
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JPH0742185B2 - Compost manufacturing method and device - Google Patents

Compost manufacturing method and device

Info

Publication number
JPH0742185B2
JPH0742185B2 JP4093855A JP9385592A JPH0742185B2 JP H0742185 B2 JPH0742185 B2 JP H0742185B2 JP 4093855 A JP4093855 A JP 4093855A JP 9385592 A JP9385592 A JP 9385592A JP H0742185 B2 JPH0742185 B2 JP H0742185B2
Authority
JP
Japan
Prior art keywords
storage tank
compost
liquid
raw material
water
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.)
Expired - Lifetime
Application number
JP4093855A
Other languages
Japanese (ja)
Other versions
JPH05270961A (en
Inventor
修一 汐見
Original Assignee
株式会社リベラル
三昭フーズ株式会社
有限会社南部興業
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 株式会社リベラル, 三昭フーズ株式会社, 有限会社南部興業 filed Critical 株式会社リベラル
Priority to JP4093855A priority Critical patent/JPH0742185B2/en
Publication of JPH05270961A publication Critical patent/JPH05270961A/en
Publication of JPH0742185B2 publication Critical patent/JPH0742185B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Landscapes

  • Treatment Of Sludge (AREA)
  • Fertilizers (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Processing Of Solid Wastes (AREA)

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】この発明は、人糞、牛糞、豚糞、
鶏糞などの家畜糞や、屎尿処理残渣や、魚介野菜類の処
理屑や残飯類などから乾燥した粉末状の堆肥を製造する
方法及び装置に関する。
BACKGROUND OF THE INVENTION The present invention relates to human feces, cow feces, pig feces,
The present invention relates to a method and an apparatus for producing dried powder compost from livestock manure such as chicken manure, human waste treatment residues, treated wastes of seafood and vegetables, and leftover rice.

【0002】[0002]

【従来の技術】従来、家畜糞などに菌種を混入し、これ
を貯蔵して発酵、分解、乾燥させ、粉末状の堆肥を製造
することが行なわれていた。
2. Description of the Related Art Conventionally, it has been practiced to mix a bacterial species in livestock manure, store it, ferment it, decompose it, and dry it to produce powdered compost.

【0003】[0003]

【発明が解決しようとする課題】ところが、市販されて
いる菌種は、これに含まれている菌の大部分が死滅して
いて生菌の含有率が低く、そのために多量の菌種が必要
になってその購入費用が無視できない値になること、及
び発酵、分解が終了するまでに6〜8ケ月の長期間を要
すること、及び出来上った堆肥は水分が多く、そのため
に取扱いに難渋すること等の問題があった。この発明
は、短期間に乾燥粉末状で取扱いに便利な堆肥を製造し
ようとするものである。
However, in the commercially available bacterial species, most of the bacteria contained therein are dead and the content rate of viable bacteria is low, and therefore a large amount of bacterial species is required. The purchase cost becomes a non-negligible value, and it takes a long time of 6 to 8 months to complete fermentation and decomposition, and the finished compost has a lot of water, which makes it difficult to handle. There was a problem such as doing. The present invention is intended to produce a compost in a dry powder form which is convenient for handling in a short period of time.

【0004】[0004]

【課題を解決するための手段】この発明は、動物糞より
堆肥製造に必要な元菌体を得る第1の工程と、これから
菌を多量に含む菌液を得る第2の工程と、菌液から乾燥
菌体を得る第3の工程と、乾燥菌体を堆肥原料に混入し
て堆肥を得る第4の工程とよりなる。
The present invention is directed to a first step for obtaining original bacterial cells required for compost production from animal feces, a second step for obtaining a bacterial solution containing a large amount of bacteria from the original bacterial cells, and a bacterial solution. And a fourth step of mixing the dried bacterial cells with the compost raw material to obtain compost.

【0005】第1の工程では、動物糞及び蛋白質原料に
水を加えて泥漿状となし、これを36〜43℃、望まし
くは38〜42℃に2〜3日間維持して、元菌体を得
る。ここで使用する蛋白質原料としては、家畜や魚介類
の内臓や血液など、食用や工業原料用として利用できな
い部分が適している。その添加量は、動物糞の10〜1
00%に相当する量が適当であり、水の添加量は動物糞
及び蛋白質原料の2〜5倍程度である。
In the first step, water is added to animal feces and protein raw material to form a slurry, which is maintained at 36 to 43 ° C., preferably 38 to 42 ° C. for 2 to 3 days to recover the original bacterial cells. obtain. As the protein raw material used here, a portion that cannot be used for food or industrial raw materials such as internal organs and blood of livestock and seafood is suitable. The amount added is 10 to 1 of animal feces.
A suitable amount is 00%, and the amount of water added is about 2 to 5 times that of animal feces and protein raw materials.

【0006】第2の工程では、第1の工程で得た泥漿状
の元菌体を更に水で希釈して液状となし、これを36〜
43℃、望ましくは38〜42℃に維持しながらエアレ
ーションを行い、菌液を得る。この所要時間は数時間乃
至一昼夜ほどである。
In the second step, the sludge-like original bacterial cells obtained in the first step are further diluted with water to form a liquid,
Aeration is performed while maintaining the temperature at 43 ° C, preferably 38 to 42 ° C to obtain a bacterial solution. This time is several hours to one day.

【0007】第3の工程では、第2の工程で得た菌液を
植物質微細片に含浸させ、これを攪拌しながら温風を送
風し、乾燥菌体を得る。ここで使用する植物質微細片と
しては、おが屑、もみがら、微細に截断した紙やわらな
どが適当であり、必要に応じ糖密や生ごみなども添加す
る。この工程の所要時間は半日乃至2日程度である。
In the third step, the plant solution is impregnated with the bacterial solution obtained in the second step, and hot air is blown while stirring the fine particles to obtain dried bacterial cells. As the plant fine pieces used here, sawdust, chaff, finely chopped paper or straw, etc. are suitable, and sugar-tightness and raw garbage are added as necessary. The time required for this process is about half a day to 2 days.

【0008】第4の工程では、第3の工程で得た乾燥菌
体を堆肥原料中に分散させて貯蔵し、時折ショベル等で
切返して攪拌し、粉末状の堆肥を得る。この所要期間は
半月乃至2ケ月程である。堆肥原料としては、動物糞、
屎尿処理施設の処理残渣、魚介野菜類の処理屑、残飯類
等を使用することができる。
In the fourth step, the dried microbial cells obtained in the third step are dispersed and stored in a compost raw material, occasionally turned over by a shovel or the like and stirred to obtain a powdery compost. This required period is about half a month to two months. Animal manure,
It is possible to use the processing residue of the human waste processing facility, the processing waste of the seafood vegetables, the leftover food and the like.

【0009】[0009]

【作用】第1の工程では、動物糞中の大腸菌が、蛋白質
原料を養分にして増殖し、第2の工程ではエアレーショ
ンにより発泡しながら更に旺盛に増殖する。このように
して得た菌液を、そのまま堆肥原料に混ぜると、堆肥原
料は泥状になって処理が一層困難になるので、第3の工
程ではこれを一旦植物質微細片に含浸させ、温風にさら
して攪拌することにより、菌を一層増殖させると共に植
物質も分解させ、乾燥菌体を得る。
In the first step, Escherichia coli in animal feces grows by using the protein raw material as a nutrient, and in the second step, the Escherichia coli grows vigorously while foaming by aeration. If the bacterial liquid thus obtained is directly mixed with the compost raw material, the compost raw material becomes muddy and the treatment becomes more difficult. Therefore, in the third step, the plant fine particles are impregnated once with By exposing to air and stirring, the bacteria are further proliferated and the plant matter is decomposed to obtain dry cells.

【0010】第4の工程では、菌体が乾燥粉末状である
ため、容易に万べんに堆肥原料中に分散させることがで
きる。貯蔵中、堆肥原料は発酵して発熱するので、週に
一回程度ショベルで切返しを行うことにより、温度を6
0〜68℃に抑え、かつ全体を一様に発酵、分解させ、
かつ乾燥させることができる。
In the fourth step, since the bacterial cells are in the form of dry powder, they can be easily dispersed in the compost raw material. During storage, the compost raw materials ferment and generate heat, so by turning them around with a shovel about once a week,
Keep it at 0-68 ℃, and ferment and decompose it uniformly,
And can be dried.

【0011】3〜4週間後には、堆肥原料は完全に分解
し、かつ自己発熱のために乾燥して、黒褐色の粉末堆肥
に変わる。その間に発生するメタンガスは、貯蔵室の上
部から取出して、良質の燃料として利用することができ
る。第2の工程におけるエアレーション用の空気や、第
3の工程における送風用の空気を、このメタンガスの燃
焼熱によって加熱することもできる
After 3 to 4 weeks, the compost raw material is completely decomposed, and is dried due to self-heating, and turns into a blackish brown powder compost. The methane gas generated during that time can be taken out from the upper part of the storage chamber and used as high quality fuel. The air for aeration in the second step and the air for blowing in the third step can be heated by the heat of combustion of the methane gas.

【0012】[0012]

【実施例】図1において、上部に投入口11を有する貯
槽10内に、蛋白質原料としての烏賊の内臓1kgと、
牛糞5kgと、水16リットルとを混合して収容し、温
度を40±2℃に設定した投込ヒーター12により加温
し、48時間培養することによって大腸菌を増殖させ
る。13はこの混合物を示す。
EXAMPLE In FIG. 1, 1 kg of squid viscera serving as a protein raw material was placed in a storage tank 10 having an inlet 11 at the top.
5 kg of cow dung and 16 liters of water are mixed and housed, heated by the throw-in heater 12 whose temperature is set to 40 ± 2 ° C., and cultured for 48 hours to grow Escherichia coli. 13 shows this mixture.

【0013】このようにして得た元菌体は、貯槽10の
下部に設けた排出管14のバルブ15を開いて貯槽20
へ移す。貯槽20は、空気抜孔21及び電動攪拌機22
を備えた蓋23を有し、かつ内部に加熱用ヒーター24
及びエアレーション用のパイプ25を有する。上述の元
菌体は、500リットルの水で希釈される。この希釈液
26をヒーター24によって40±2℃に加温し、パイ
プ25より空気を送入してエアレーションを行うと、希
釈液26は激しく発酵して液面に泡を生じ、7〜8時間
後に菌が増殖した菌液が得られる。
The original bacterial cells thus obtained are stored in the storage tank 20 by opening the valve 15 of the discharge pipe 14 provided in the lower portion of the storage tank 10.
Move to. The storage tank 20 includes an air vent hole 21 and an electric stirrer 22.
Having a lid 23 provided with a heater 24 for heating inside
And a pipe 25 for aeration. The above-mentioned original cells are diluted with 500 liters of water. When this dilution liquid 26 is heated to 40 ± 2 ° C. by the heater 24 and air is fed through the pipe 25 to perform aeration, the dilution liquid 26 fermented violently to generate bubbles on the liquid surface for 7 to 8 hours. After that, a bacterial solution in which the bacteria have grown is obtained.

【0014】30は貯槽で底の上方に金網31が張ら
れ、金網31の下方に送気管32が設けられており、金
網31の上方には電動攪拌機33が配置されている。こ
の貯槽30に、おが屑0.5tと糖密30kgとを投入
して培地34を造り、貯槽20の下部の排出管27のバ
ルブ28を開いて培地34に菌液を混入する。貯槽30
にシート35を被せ、攪拌機33によって培地34を攪
拌しながら送気管32から40℃の温風を送入すると、
培地34は発酵して24時間後には濃褐色に変色し、か
つ乾燥して乾燥菌体に変化する。
Reference numeral 30 denotes a storage tank, in which a wire net 31 is stretched above the bottom, an air supply pipe 32 is provided below the wire net 31, and an electric stirrer 33 is arranged above the wire net 31. 0.5 t of sawdust and 30 kg of sugar-tightness are put into this storage tank 30 to make a medium 34, and the valve 28 of the discharge pipe 27 at the bottom of the storage tank 20 is opened to mix the bacterial solution into the medium 34. Storage tank 30
When the sheet 35 is covered with and the medium 34 is stirred by the stirrer 33 and hot air of 40 ° C. is fed from the air pipe 32,
The medium 34 turns fermented into dark brown after 24 hours of fermentation, and is dried to change to dry cells.

【0015】40は貯蔵室で、幅4m、奥行4m、高さ
3mの寸法を有し、前面に扉41が設けられている。こ
の貯蔵室40に牛糞46tを収容し、貯槽30の金網3
1に設けたホッパ36のゲート37を開いて乾燥菌体を
牛糞上に落し、ショベルで混合し発酵させる。乾燥菌体
を混入した牛糞42は、発酵熱により60〜68℃に昇
温し、これにより発酵は更に促進される。
A storage room 40 has a width of 4 m, a depth of 4 m, and a height of 3 m, and is provided with a door 41 on the front surface. This storage room 40 accommodates 46 t of cow dung, and the wire net 3 of the storage tank 30.
The gate 37 of the hopper 36 provided in No. 1 is opened to drop the dried bacterial cells on cow dung, which is mixed with a shovel and fermented. The cow dung 42 mixed with the dried microbial cells is heated to 60 to 68 ° C. by the heat of fermentation, whereby the fermentation is further promoted.

【0016】1週間ごとに牛糞をショベルで切返すこと
によって発酵は均一に進み、3〜4週間後には発酵熱に
よって乾燥して黒褐色の粉末状の堆肥に変化する。
By excavating the cow dung every week, the fermentation progresses uniformly, and after 3 to 4 weeks, it is dried by the heat of fermentation and changed into a blackish brown powdery compost.

【0017】このようにして得た堆肥は、乾燥した粉末
状であるために取扱いが極めて容易であり、完全に分解
しているために植物を傷めず、かつ土壌の保水力及び通
気性を改善し、その有効肥料成分は植物の養分となる。
Since the compost thus obtained is in the form of a dry powder, it is extremely easy to handle, and because it is completely decomposed, it does not damage the plants and improves the water retention and air permeability of the soil. However, the effective fertilizer component becomes a nutrient for plants.

【0018】牛糞42は、発酵中に多量のメタンを発生
する。よって、貯蔵室40の天井に設けた排出管43よ
りこれを取出して、良質の燃料として使用することがで
きる。貯槽30において送気管32から送入する温風に
は、このメタンを熱源として利用することができる。
The cow dung 42 produces a large amount of methane during fermentation. Therefore, this can be taken out from the discharge pipe 43 provided on the ceiling of the storage chamber 40 and used as a high-quality fuel. This methane can be used as a heat source for the warm air sent from the air supply pipe 32 in the storage tank 30.

【0019】[0019]

【発明の効果】以上のように、この発明によるときは、
人糞、家畜糞、屎尿処理残渣、魚介野菜類処理屑、残飯
類などの含水量の多い生の堆肥原料を、短期間内に完全
に発酵、分解し、かつ乾燥した粉末状の堆肥に変えるこ
とができ、その堆肥は取扱いが容易で、有効肥料成分に
富み、植物に全く無害で、かつ土壌改良に貢献するもの
である。
As described above, according to the present invention,
Raw compost raw materials with high water content, such as human dung, livestock dung, manure treatment residue, seafood and vegetable treatment wastes, and leftover rice, are completely fermented and decomposed within a short period of time, and converted into dry powder compost. The compost is easy to handle, rich in effective fertilizer components, completely harmless to plants, and contributes to soil improvement.

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

【図1】本発明の実施例の説明図である。FIG. 1 is an explanatory diagram of an embodiment of the present invention.

【符号の説明】[Explanation of symbols]

10 第1の貯槽 12 投込ヒーター(加熱手段) 20 第2の貯槽 22 攪拌機 24 ヒーター 25 エアレーション用送気管 30 第3の貯槽 31 金網 32 温風送気管(加熱手段及び空気送入手段) 33 攪拌機 40 貯蔵室 10 1st storage tank 12 Immersion heater (heating means) 20 2nd storage tank 22 Stirrer 24 Heater 25 Air supply pipe for aeration 30 3rd storage tank 31 Wire mesh 32 Hot air supply pipe (heating means and air supply means) 33 Stirrer 40 storage room

───────────────────────────────────────────────────── 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 C05F 9/00 7188−4H C12N 1/14 Z 7236−4B ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location C05F 9/00 7188-4H C12N 1/14 Z 7236-4B

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 動物糞及び蛋白質原料に泥漿状に水を加
え36〜43℃で保持して元菌体を得る第1の工程と、
この元菌体を液状に水で希釈しエアレーション下で36
〜43℃で保持して菌液を得る第2の工程と、この菌液
を十分湿潤状態に植物質微細片に含浸させてこの含浸物
に温風を送風しながら攪拌して乾燥菌体を得る第3の工
程と、この乾燥菌体を混入した堆肥原料を長時間貯蔵し
て乾燥粉末状堆肥を得る第4の工程とよりなることを特
徴とする堆肥製造方法。
1. A first step in which water is added to animal feces and protein raw material in the form of sludge and kept at 36 to 43 ° C. to obtain original cells.
Dilute the original cells with water and add 36 under aeration.
The second step of obtaining a bacterial liquid by holding at ~ 43 ° C, and impregnating the bacterial microbe with the bacterial liquid in a sufficiently wet state, and agitating the impregnated product while blowing warm air to dry the bacterial cells. A compost manufacturing method comprising: a third step of obtaining and a fourth step of storing the compost raw material mixed with the dry cells for a long time to obtain a dry powder compost.
【請求項2】 泥漿状に水で希釈された動物糞及び原料
蛋白質を収容しこれを36〜43℃に加温する加熱手段
を備えた第1の貯槽と、第1の貯槽の内容物を水で液状
に希釈した液体を収容しこれを36〜43℃に加温する
加熱手段とエアレーション手段と攪拌手段とを備えた第
2の貯槽と、第2の貯槽の内容液を含浸させた植物質微
細片を収容しこれに対する加熱手段と空気送入手段と攪
拌手段とを備えた第3の貯槽と、第3の貯槽の内容物を
混入した堆肥原料を貯蔵する貯蔵室とよりなることを特
徴とする堆肥製造装置。
2. A first storage tank having a heating means for containing animal feces and raw material proteins diluted with water in a sludge form and heating the protein to 36 to 43 ° C., and the contents of the first storage tank. A second storage tank provided with a heating means, an aeration means, and a stirring means for accommodating a liquid diluted to a liquid state with water and heating the liquid to 36 to 43 ° C., and a plant impregnated with the liquid content of the second storage tank It comprises a third storage tank for accommodating fine particles and having a heating means, an air feeding means, and a stirring means, and a storage chamber for storing the compost raw material mixed with the contents of the third storage tank. Characteristic compost manufacturing equipment.
JP4093855A 1992-03-19 1992-03-19 Compost manufacturing method and device Expired - Lifetime JPH0742185B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4093855A JPH0742185B2 (en) 1992-03-19 1992-03-19 Compost manufacturing method and device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4093855A JPH0742185B2 (en) 1992-03-19 1992-03-19 Compost manufacturing method and device

Publications (2)

Publication Number Publication Date
JPH05270961A JPH05270961A (en) 1993-10-19
JPH0742185B2 true JPH0742185B2 (en) 1995-05-10

Family

ID=14094039

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4093855A Expired - Lifetime JPH0742185B2 (en) 1992-03-19 1992-03-19 Compost manufacturing method and device

Country Status (1)

Country Link
JP (1) JPH0742185B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009154104A (en) * 2007-12-27 2009-07-16 Sumitomo Osaka Cement Co Ltd Organic waste slurry storage method and fuel conversion method, biomass fuel, and organic waste slurry storage device

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JP2009154104A (en) * 2007-12-27 2009-07-16 Sumitomo Osaka Cement Co Ltd Organic waste slurry storage method and fuel conversion method, biomass fuel, and organic waste slurry storage device

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