JPS6138697A - Treatment of waste materal having high water content by yeast cultivating fermetation - Google Patents

Treatment of waste materal having high water content by yeast cultivating fermetation

Info

Publication number
JPS6138697A
JPS6138697A JP16088384A JP16088384A JPS6138697A JP S6138697 A JPS6138697 A JP S6138697A JP 16088384 A JP16088384 A JP 16088384A JP 16088384 A JP16088384 A JP 16088384A JP S6138697 A JPS6138697 A JP S6138697A
Authority
JP
Japan
Prior art keywords
fermentation
yeast
water content
waste
treatment
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
Application number
JP16088384A
Other languages
Japanese (ja)
Inventor
Tsutomu Takeshita
竹下 力
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP16088384A priority Critical patent/JPS6138697A/en
Publication of JPS6138697A publication Critical patent/JPS6138697A/en
Pending legal-status Critical Current

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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

  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)
  • Fertilizers (AREA)

Abstract

PURPOSE:To enable efficient treatment of waste material having high water content such as domestic garbage with yeast by mixing yeast with the waste material. CONSTITUTION:Raw night soil is fed to a fermentation tank 11. The water content of the raw night soil is adjusted by mixing dry night soil, and first seed yeast consisting of brewing yeast is charged to the mixture and stirred. The temp. is elevated to at highest 65 deg.C when the height of the accumulated night soil is 15cm, and the temp. falls to 45 deg.C after 3-4 days. When it is <=45 deg.C, fermentation dying is continued while continuing stirring to finish the treatment. The product is finally discharged from the fermentation tank 11 and packed in bags.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 この発明は新規な酵母培養型醗酵による高水分含有廃棄
物の処理方法に関し、醸造用酵母を配合して醗酵させる
ことにより、人畜糞尿、家庭残渣等の高水分含有廃棄物
を短期間番;効率よく醗酵処理及び水分除去するととも
に、処理後の醗酵生成物をタネ菌として再利用すること
ができ、またそのまま肥料として農地に還元することの
できる酵母培養型醗酵による高水分含有廃棄物の処理方
法を提供せんとするものである。
[Detailed Description of the Invention] [Field of Industrial Application] This invention relates to a method for treating high moisture content waste using a novel yeast culture type fermentation. High moisture content waste such as residue can be processed for a short period of time; in addition to efficiently fermenting and removing moisture, the fermented product after treatment can be reused as seed fungi, and can also be directly returned to farmland as fertilizer. The purpose of the present invention is to provide a method for treating high moisture content waste using yeast culture type fermentation.

〔従来の技術〕[Conventional technology]

従来1人畜糞尿、家庭残渣等の高水分含有廃棄物は、そ
のまま畑等に埋め込んだり散布したりして土壌側;還元
していた。しかしながら、この場合には農作物に生育障
害を起こすことが多く、また衛生的、環境的に多くの弊
害が発生して社会問題化していた。このため天日乾燥し
たり、オガクズ、プレナークズ、チップダスト等の木粉
、あるいはモミガラ等を配合したりして水分を調節し、
堆肥化すること番;よって有機質肥料や土壌改良剤とし
て土壌に還元することが、広く行われている。
Conventionally, wastes containing high moisture content, such as human and livestock manure and household residue, have been reduced to the soil by burying or scattering them in fields, etc. as they are. However, in this case, growth problems often occur in agricultural crops, and many hygienic and environmental problems occur, resulting in social problems. For this reason, the moisture content is adjusted by drying in the sun or by adding wood flour such as sawdust, planar scum, chip dust, or rice hulls.
Therefore, it is widely practiced to compost it and return it to the soil as an organic fertilizer or soil conditioner.

人畜糞尿、家庭残渣等の高水分含有廃棄物の堆肥化は、
上記混合素材による水分調整のほか、天日乾燥または火
力により高水分含有廃棄物の水分を60%に調節した後
、堆積発熱をまって三日に一回の割合で切返しを行うこ
と等、充分な好気的条件を与えることにより60〜70
℃以上に昇温し、約2〜3週間で醗酵は完了する。
Composting high moisture content waste such as human and animal manure and household residue is
In addition to adjusting the moisture content using the above-mentioned mixed materials, it is also possible to adjust the moisture content of high-moisture waste to 60% by sun drying or thermal power, and then turn it over once every three days to allow the heat buildup to occur. 60-70 by providing aerobic conditions
Fermentation is completed in about 2 to 3 weeks when the temperature is raised above ℃.

これは、堆肥化の当初に微生・物菌体の増殖とともに、
有機酸その他の生成、酸素の活発な消費を伴う有機物分
解の第1段階があり、この環元的性格を持つ段階では、
未熟のため作物の生育障害を起こすので、植物の生育環
境としては不都合なためである。この第1段階から、ア
ンモニア態窒素が亜硝酸態を経て硝酸態へと変化する第
2段階に移行するが、この段階は酸化的性格を持ってい
てゆっくり長く進行するもので、おおむね4〜6ケ月の
期間を必要とした。
This is due to the proliferation of microorganisms and bacteria at the beginning of composting.
There is a first stage of organic matter decomposition that involves the production of organic acids and other substances and the active consumption of oxygen.
This is because the immaturity causes problems in the growth of crops, making it an inconvenient growing environment for plants. From this first stage, the ammonia nitrogen changes to the nitrite state through the nitrite state, which is the second stage, but this stage has an oxidative character and progresses slowly and over a long period of time. It took several months.

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

しかしながら、温度が60〜70℃以上の良好な堆肥化
を行うためには、堆積層の厚さを約1m、長さを2m以
上とすることが要求され、この堆積層を切り返すために
は大がかりで高価な攪拌装置、または約2〜3週間の長
期間にわたる送風あるいは切返し等の手間がかかってい
た。
However, in order to achieve good composting at a temperature of 60 to 70°C or higher, the thickness of the deposited layer must be approximately 1 m and the length must be at least 2 m, and cutting back this deposited layer requires extensive work. This requires an expensive stirring device, or a long period of about 2 to 3 weeks of air blowing or turning.

〔問題点を解決するための手段〕[Means for solving problems]

この発明の酵母培養型醗酵による高水分含有廃棄物の処
理方法はこのような事情に鑑み、人畜糞尿、家庭残渣等
の高水分含有廃棄物に醸造用酵母を配合することにより
従来例の上記欠点を解消したものである。
In view of these circumstances, the method of treating high moisture content waste by yeast culture fermentation of the present invention solves the above-mentioned drawbacks of the conventional method by blending brewing yeast into high moisture content waste such as human and animal excrement and household residue. .

すなわち、人畜糞尿、家庭残渣等の高水分含有廃棄物を
所定の水分含有量に調節した後、醸造用酵母を配合して
醗酵させることを特徴とする、酵母培養型醗酵による高
水分含有廃棄物の処理方法である。
That is, high moisture content waste by yeast culture type fermentation, which is characterized in that high moisture content waste such as human and animal excrement and household residue is adjusted to a predetermined moisture content, and then brewing yeast is mixed and fermented. This is the processing method.

この発明において酵母培養型醗酵とは、活動力の極めて
旺盛な酵母による醗酵方法であって、次のようなタイプ
が明らかになっている。
In this invention, yeast culture fermentation is a fermentation method using highly active yeast, and the following types have been clarified.

■、極めて好気的で酸素の要求率が高く、水分含有率6
0%前後の状態では、分解する炭水化物、特にデンプン
の存在する場合には、第3図に示すような床面堆積で約
15cmの条件のときに65℃の温度が得ら九た。図中
//は醗酵層、/dは未醗酵層、/3は醗酵床である。
■ Extremely aerobic, with high oxygen demand and water content of 6
At around 0%, in the presence of decomposing carbohydrates, especially starch, a temperature of 65° C. was obtained under conditions of about 15 cm of floor deposition as shown in FIG. In the figure, // is a fermentation layer, /d is an unfermented layer, and /3 is a fermentation bed.

■、■で示すように極めて好気的な特性から、はとんど
従来の例が示すような嫌気的(環元的)な特徴を見せな
い。すなわち、悪臭の根源である有機酸臭や硫化水素臭
等の、悪臭公害の元凶となる物質の発生をみない。
As shown in ■ and ■, it has extremely aerobic characteristics, so it hardly shows the anaerobic (cyclonetic) characteristics shown in conventional examples. In other words, the generation of substances that are the cause of odor pollution, such as organic acid odor and hydrogen sulfide odor, which are the sources of odor, is not observed.

■1人畜糞尿、家庭残渣等の高水分含有廃棄物における
窒寿と炭素の比率が小さい場合、その醗酵による発熱速
度は速く、極めて短時間に易溶解性の炭水化物の分解が
終わり、発熱は急速に降下する。この時、窒素分はアン
モニアガスとして分離され、排気中に混入することがあ
るが。
■1 When the ratio of nitric life to carbon in high-moisture content waste such as human animal manure and household residue is small, the rate of heat generation due to fermentation is fast, and the decomposition of easily soluble carbohydrates is completed in an extremely short period of time, and the heat generation is rapid. descend to At this time, nitrogen is separated as ammonia gas and may be mixed into the exhaust gas.

特に強いという印象はない。その排気中の主成分は炭酸
ガス(CO2)である。
I don't get the impression that it's particularly strong. The main component of the exhaust gas is carbon dioxide (CO2).

人畜糞尿、家庭残渣等の高水分含有廃棄物が、嫌気的状
態におかれた場合に悪臭を放つようなものでも、この酵
母培養型醗酵により処理すれば、2〜3日で完全に脱臭
することができる。
Even if high moisture content waste such as human and animal excrement and household residue gives off a bad odor when placed in an anaerobic condition, if it is processed using this yeast culture type fermentation, the odor will be completely deodorized in 2 to 3 days. be able to.

■本醗酵は空気、すなわち酸素を充分に供給することで
完全な機能を果す。しかしながら過剰な酸素供給はマイ
ナス要因となる。すなわち、醗酵素材の急激な温度低下
、水分の過剰な一時的放出等により醗酵中止、または醗
酵機能をいちじるしく低下させる。
■Main fermentation works perfectly by supplying a sufficient amount of air, or oxygen. However, excessive oxygen supply becomes a negative factor. That is, a sudden temperature drop in the enzyme material, excessive temporary release of water, etc. may cause the fermentation to stop or the fermentation function to be significantly reduced.

したがって微風程度の空気の流れが最適な空気の供給条
件といえる。
Therefore, it can be said that the optimal air supply condition is an air flow of a slight breeze.

本発明で使用する醸造用酵母としては、種々の醸造用酵
母のほか、酒かす、みりん醸造かす等が挙げられる。
Examples of the brewing yeast used in the present invention include various brewing yeasts, sake lees, mirin brewing lees, and the like.

〔実施例〕〔Example〕

以下図面に基いてこの発明の酵母培養型醗酵による高水
分含有廃棄物の処理方法の一実施例を説明する。
An embodiment of the method for treating high water content waste by yeast culture fermentation according to the present invention will be described below with reference to the drawings.

先ず、第1図のフローシートに基いて説明する。First, explanation will be given based on the flow sheet shown in FIG.

この発明においては、醗酵と攪拌とを単ゴの醗酵槽で行
うことができる。   □ イ、用意された生糞法を醗酵槽に搬入する。
In this invention, fermentation and stirring can be performed in a single fermentation tank. □ A. Transport the prepared raw feces method to the fermentation tank.

口、この醗酵素材に乾燥糞尿を混合して水分を調整する
とともに、醸造用酵母からなる第1のタネ菌を投入して
攪拌混合する。
First, dry manure and urine are mixed with this enzyme material to adjust the moisture content, and a first seed bacterium consisting of brewing yeast is added and mixed with stirring.

固液分離機を珀いるときは、分離して得た固形物に醸造
用酵母を添加して植菌し、攪拌する。
When passing through the solid-liquid separator, brewer's yeast is added to the solid material obtained by separation, inoculated, and stirred.

液状物は貯溜槽に導いてポンプにより、醗酵状況と乾燥
の度合とに応じて表面に散布する。
The liquid is introduced into a storage tank and sprayed onto the surface using a pump depending on the fermentation situation and degree of dryness.

ハ、醗酵は種菌後約24時間以内に始まり、最高温度は
15cmの堆積で65℃に昇温し、3〜4日で45℃に
降温する。これは水分不足と栄葉不足が原因となるので
、生糞法または上記液状物の全面散布を行うと再び昇温
させることができる。
C. Fermentation begins within about 24 hours after inoculum, and the maximum temperature rises to 65°C with 15 cm of accumulation, and decreases to 45°C in 3 to 4 days. This is caused by a lack of moisture and a lack of foliage, so the temperature can be raised again by using the raw feces method or by spraying the above-mentioned liquid over the entire surface.

二、45℃以下に下がったら、攪拌を続けながら醗酵乾
燥を続け、仕上げを行う。ここまでの期間はlO〜15
日前後見れば良い。
2. When the temperature drops below 45°C, continue fermentation and drying while stirring to finish. The period so far is lO ~ 15
Just look around the day.

二、その後醗酵槽から搬出して、 ホ0袋詰めをする。2. After that, remove it from the fermenter, Pack 0 bags.

乾燥前の段階のものは、すでに醸造用酵母の繁殖が充分
行われているので、再度種菌として使用することができ
る。
Since brewing yeast has already sufficiently propagated in the pre-drying stage, it can be used again as a starter.

この発明の酵母培養型醗酵番;よる高水分含有廃棄物の
処理方法の他の実施例における乾燥装置を第2図に示す
。この例では攪拌、送風をほとんど使用せず、40cm
間隔に空間ICl11をもつ立体的な醗酵槽、2/内で
行う。この場合、嫌気的醗酵の条件をまったくなくして
しまうため、悪臭が発生しにくい。さらに施設的には立
体的な槽となるため、広い面積は必要としない。また攪
拌も不要となり。
FIG. 2 shows a drying apparatus in another embodiment of the method for treating high moisture content waste using yeast culture fermentation according to the present invention. In this example, stirring and blowing are hardly used, and the 40 cm
The fermentation is carried out in a three-dimensional fermenter, 2/, with a space ICl11 in between. In this case, the conditions for anaerobic fermentation are completely eliminated, so bad odors are less likely to occur. Furthermore, since the facility is a three-dimensional tank, a large area is not required. Also, stirring is no longer necessary.

そのための動力も必要としない。No power is required for that purpose.

上記乾燥装置は、醗酵槽、、2/からの発熱を吸引パイ
プ、、2tIで抜き取り、床面認3を加温して天日と大
気の熱で乾燥させる。、2.2は排気パイプである。
The drying device extracts the heat generated from the fermentation tank 2/ with a suction pipe 2tI, heats the floor surface 3, and dries it using the heat of the sun and the atmosphere. , 2.2 is an exhaust pipe.

〔作用〕[Effect]

この発明の酵母培養型醗酵による高水分含有廃棄物の処
理方法の作用番〔ついて説明する。
The operation of the method for treating high water content waste by yeast culture fermentation according to the present invention will be explained.

(。(.

醸造用酵母により、従来例の第1段階の環元的性格の段
階をほとんど経ないで醗酵させるので、急激に、しかも
60〜70℃の高温に昇温させることかでき、雑草のタ
ネや各種雑菌、害虫のウジやタマゴ等が死滅するので、
極めて衛生的で、安全な処理物が得られる。
Since fermentation is carried out using brewer's yeast without passing through the conventional first stage, which has a cyclic nature, it is possible to rapidly raise the temperature to a high temperature of 60 to 70 degrees Celsius, which can produce weed seeds and various Bacteria, pests such as maggots and eggs are killed,
Extremely hygienic and safe processed materials can be obtained.

また醗酵、乾燥して得た処理物は、粒度が均一で肥効の
高い有機肥料となる。
Furthermore, the processed product obtained by fermentation and drying becomes an organic fertilizer with uniform particle size and high fertilizing effect.

〔発明の効果〕〔Effect of the invention〕

この発明の酵母培養型醗酵による高水分含有廃棄物の処
理方法は以上のように構成したので、醗酵の期間が短縮
でき、しかも環元的性格の醗酵段階がないので悪臭や有
毒ガスの発生がない。
Since the method of treating high moisture content waste by yeast culture fermentation according to the present invention is configured as described above, the fermentation period can be shortened, and since there is no fermentation step of a cyclic nature, no foul odor or toxic gas is generated. do not have.

また取扱いが簡単であり、複雑な施設を必要としないの
で大幅な自動化が可能となるだけでなく、処理施設の極
めて大幅なコストダウンを行うことができる。
Furthermore, since it is easy to handle and does not require complicated facilities, it not only allows for extensive automation, but also enables extremely significant cost reductions in processing facilities.

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

第1図はこの発明の酵母培養型醗酵による高水分含有廃
棄物の処理方法の一実施例を示すフロー図、第2図は本
発明において用いられる醗酵装置の斜視図、第3図はこ
の発明の醗酵機構を示す断面図である。 l/・・・醗酵層     /、2・・・未醗酵層/3
・・・醗酵床 =?/・・・醗酵槽     2.2・・・排気パイプ
、23・・・床面 第1図 第2図 J 第3図 (、円)        昭和59年 11月 12日
昭和59年特 許 願第 /イρF?ρθ号2 発明の
名称 酵母培養型醗酵による高水分含有廃棄物の処理方法 3 補正をする者 事件との関係  特許出願人 住所(居所)山梨県西八代郡上九−色村富士ケ4代理人
〒400 昭和  年  月  日(発送日) 6 補正により増加する発明の数 8 補正の内容 1) 明細書第3頁第1行目、同第8頁第9行目および
同第20行目の「還元的性格」を、「還元的性格」と訂
正する。 2) 明細書第6頁第19行目の「種菌Jを、「植菌」
と訂正する。
FIG. 1 is a flow diagram showing an embodiment of the method for treating high moisture content waste by yeast culture fermentation according to the present invention, FIG. 2 is a perspective view of the fermentation apparatus used in the present invention, and FIG. FIG. 2 is a cross-sectional view showing the fermentation mechanism. l/...Fermented layer/, 2...Unfermented layer/3
...Fermentation bed=? /...Fermentation tank 2.2...Exhaust pipe, 23...Floor surface Figure 1 Figure 2 Figure J Figure 3 (, yen) November 12, 1980 Patent Application No. / IρF? ρθ No. 2 Name of the invention Method for treating high moisture content waste by yeast culture fermentation 3 Relationship with the case of the person making the amendment Patent applicant address (residence) Kamikyu, Nishiyatsushiro-gun, Yamanashi Prefecture - Iromura Fujike 4 Agent address 400 Showa year, month, day (shipment date) 6 Number of inventions increased by the amendment 8 Contents of the amendment 1) “Reductive "personality" is corrected to "reductive personality." 2) "Inoculation of seed culture J" on page 6, line 19 of the specification
I am corrected.

Claims (1)

【特許請求の範囲】[Claims] 1、人畜糞尿、家庭残渣等の高水分含有廃棄物を所定の
水分含有量に調節した後、醸造用酵母を配合して、醗酵
させることを特徴とする酵母培養型醗酵による高水分含
有廃棄物の処理方法。
1. High-moisture-containing waste by yeast culture fermentation, which is characterized by adjusting high-moisture-containing waste such as human and animal excrement and household residue to a predetermined moisture content, and then fermenting it by blending brewing yeast. processing method.
JP16088384A 1984-07-31 1984-07-31 Treatment of waste materal having high water content by yeast cultivating fermetation Pending JPS6138697A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP16088384A JPS6138697A (en) 1984-07-31 1984-07-31 Treatment of waste materal having high water content by yeast cultivating fermetation

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP16088384A JPS6138697A (en) 1984-07-31 1984-07-31 Treatment of waste materal having high water content by yeast cultivating fermetation

Publications (1)

Publication Number Publication Date
JPS6138697A true JPS6138697A (en) 1986-02-24

Family

ID=15724429

Family Applications (1)

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JP16088384A Pending JPS6138697A (en) 1984-07-31 1984-07-31 Treatment of waste materal having high water content by yeast cultivating fermetation

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4995292A (en) * 1988-03-22 1991-02-26 Casio Computer Co., Ltd. String vibration detecting device for electronic stringed instrument
JPH0672788A (en) * 1992-06-16 1994-03-15 Sanko Sangyo:Yugen Production of organic fermented matter
NL1001667C2 (en) * 1995-11-16 1997-05-21 Soepenberg Beheer B V Method for homogenizing manure.
CN101811893A (en) * 2010-03-23 2010-08-25 新疆农业科学院土壤肥料与农业节水研究所 Treatment process for improving composting efficiency of domestic garbage

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5286256A (en) * 1976-01-08 1977-07-18 Hayashida Machinery Ind Odorrfree fomentation method of animal night soil
JPS52128643A (en) * 1976-04-21 1977-10-28 Mitsubishi Electric Corp Process for treating organic sludge

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5286256A (en) * 1976-01-08 1977-07-18 Hayashida Machinery Ind Odorrfree fomentation method of animal night soil
JPS52128643A (en) * 1976-04-21 1977-10-28 Mitsubishi Electric Corp Process for treating organic sludge

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4995292A (en) * 1988-03-22 1991-02-26 Casio Computer Co., Ltd. String vibration detecting device for electronic stringed instrument
JPH0672788A (en) * 1992-06-16 1994-03-15 Sanko Sangyo:Yugen Production of organic fermented matter
NL1001667C2 (en) * 1995-11-16 1997-05-21 Soepenberg Beheer B V Method for homogenizing manure.
CN101811893A (en) * 2010-03-23 2010-08-25 新疆农业科学院土壤肥料与农业节水研究所 Treatment process for improving composting efficiency of domestic garbage

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