JPH09142977A - Treatment of domestic animal dung and method for recycling the same - Google Patents

Treatment of domestic animal dung and method for recycling the same

Info

Publication number
JPH09142977A
JPH09142977A JP7309047A JP30904795A JPH09142977A JP H09142977 A JPH09142977 A JP H09142977A JP 7309047 A JP7309047 A JP 7309047A JP 30904795 A JP30904795 A JP 30904795A JP H09142977 A JPH09142977 A JP H09142977A
Authority
JP
Japan
Prior art keywords
organic
raw material
dung
treatment
calcium
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
JP7309047A
Other languages
Japanese (ja)
Inventor
Takeshi Kato
剛 加藤
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.)
IZUWA KK
Original Assignee
IZUWA KK
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 IZUWA KK filed Critical IZUWA KK
Priority to JP7309047A priority Critical patent/JPH09142977A/en
Publication of JPH09142977A publication Critical patent/JPH09142977A/en
Pending 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

Landscapes

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

Abstract

PROBLEM TO BE SOLVED: To treat a large amt. of domestic animal dung within a short period of time and to eliminate the need for waste water treatment facilities so as to save manpower and to reduce costs by incorporating a reaction agent, such as CaO, into the domestic animal dung, deodorizing the domestic animal dung by the heat generated in chemical reaction,sterilizing the dung with an alkali, dehydrating the dung, making the dung odorless by stable chlorine dioxide and maturing the dung by fermentation. SOLUTION: The flow sheet of the treating device 1 is shown in the fig. Org. waste 2, such as domestic animal dung, is charged and stored in a hopper 20 of a raw material storage house 4. A specified amt. of this waste is supplied by a supplying machine 3 into a hopper 40 of an agitation reaction vessel 7. On the other hand, calcium oxide is charged into a hopper 30 of a supplying machine 6 and is supplied to the hopper 40 at the ratio set to meet the supply rate of the org. waste 2. The raw material is charged overagely by a charging device 41. Water is sprayed to the raw material from a water spraying device 49 by a water pressure pump 54 and the raw material is agitated by an agitating machine 48 to effect the chemical reaction, by which the raw material is deodorized and sterilized. The org. waste 2A after the reaction is taken out of the tank 45 and is carried by a conveyor 60 to a yard 8 where the org. waste is turned and matured.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は、牛糞、豚糞、鶏糞
等の有機性物質を処理して再利用する家畜糞尿等の処理
法及び再利用法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 for treating and recycling livestock manure, etc., for treating and recycling organic substances such as cow dung, pig dung, and chicken dung.

【0002】[0002]

【従来の技術】従来、家畜糞尿等の処理法としては、例
えば特開昭60-191082 号(鶏糞処理法および再利用法)
や特公平7-42185 号(堆肥製造方法及び装置)などが開
示されている。前者の方法は、天然貝化石を粉末状に精
製加工された処理剤を処理原料に混合攪拌して熱風乾燥
する方法であり、後者は元菌体と歯液から成る乾燥菌体
を処理原料に混入して乾燥粉末状の堆肥を精製する方法
である。
2. Description of the Related Art Conventionally, as a method for treating livestock excrement, for example, JP-A-60-191082 (chicken dung treatment method and recycling method)
Japanese Patent Publication No. 7-42185 (compost manufacturing method and device) is disclosed. The former method is a method in which a processing agent obtained by purifying natural shell fossils into a powder form is mixed with a processing raw material and agitated, followed by hot-air drying.The latter method uses dried microbial cells composed of original cells and tooth fluid as processing raw materials. This is a method of purifying dry powdered compost by mixing.

【0003】また最近、本願出願人が開発した特願平6-
162116号(特殊肥料製造方法及びその装置)のように、
有機性廃棄物を醗酵熟成する方法が開示されている。
[0003] Recently, Japanese Patent Application No.
Like 162116 (special fertilizer production method and its equipment)
A method for fermenting and aging organic waste is disclosed.

【0004】[0004]

【発明が解決しようとする課題】このように従来の醗酵
乾燥方式による問題点、例えば醗酵させて乾燥させるだ
けでは悪臭(臭気)や殺菌(滅菌)ができない点、糞尿
による河川・地下水等の汚染を防ぐための排水浄化施設
(水質汚濁防止施設)が必要な点、野積堆積場所等での
流出・飛散現象である膨潤(安息角の不保持)が生ずる
点、などが生活環境における公害問題の要因になってい
た。
As described above, there are problems with the conventional fermentation and drying method, such as the fact that a bad odor (odor) and sterilization (sterilization) cannot be achieved by only fermenting and drying, and contamination of rivers, groundwater, etc. by manure. Of wastewater purification facilities (water pollution control facilities) to prevent water pollution, and swelling (non-retention of angle of repose) that is a phenomenon of runoff / scattering at places where deposits are accumulated, etc. It was a factor.

【0005】[0005]

【課題を解決するための手段】本発明は、上記の如き課
題を解決するために開発したものであって、牛糞、豚
糞、鶏糞の家畜糞尿等を化学分析した処理原料に酸化カ
ルシウム等の反応剤を混入した後に電子及びイオン作用
により化学反応させる処理方法において、前記化学反応
後にイオン化されているゾル状の処理原料をゲル化しか
つアンモニア(NH3 )、硫化水素(H2 S)、トリメ
チルアミン((CH3 3 N)等のガス体及び悪臭物質
を反応時の発熱で揮散して脱臭させる第1処理工程と、
該脱臭処理後にCaO(PH13)が処理原料の5%
(重量比)程度の添加剤にてアルカリ殺菌させる第2処
理工程と、該殺菌処理後に有機物質等に吸着されている
水分を固形分と分離させ更に水分をカルシウムの働きに
より表面に引き出して脱水させる第3処理工程と、前記
脱水処理後に安定二酸化塩素(ClO2 )から徐々に揮
散される酸化作用により悪臭物質を酸化させて分子構造
を分解して無臭の分子構造物質に変化させる第4処理工
程と、前記排気脱臭後に有機性処理物質を所定期間放置
しかつ該放置期間中に少なくとも1回以上の切り返しを
して醗酵熟成させる第5処理工程とから構成されること
を特徴とする家畜糞尿等の処理法の提供にあり、また家
畜糞尿等の有機性処理物質を一時貯溜させて供給機に一
定量供給する処理原料の貯溜方法と、酸化カルシウム
(CaO)を一時貯溜させて前記供給機の供給量に対し
て酸化カルシウムを一定量供給機に供給する酸化カルシ
ウムの供給方法と、前記有機性処理物質及び酸化カルシ
ウムを攪拌反応槽に投入して水の存在下で混合反応させ
る攪拌反応方法と、該攪拌反応槽から排出された有機性
廃棄物を所定時間放置するヤード及び切り返し機を介し
て醗酵させて熟成させる方法と、から構成される家畜糞
尿等の処理法の提供にある。更に、前記処理方法により
得られた有機性処理物質は、酸性土壌の中和作用、チッ
ソ・リン酸・カリウム等の肥効率の促進、葉緑素の欠乏
及び黄変防止、有効微生物及び菌体群の繁殖助長、水分
の保持及び放出(自己吸放水性等)し、有機肥料及び土
壌改良剤などに再利用できることを特徴とする家畜糞尿
等の再利用法の提供にあり、また前記有機肥料の主成分
であるテトラビロールは、有機水酸化塩、重炭酸カルシ
ウム、炭酸カルシウムの三重カプセルの内核に安定さ
せ、更に超微粒のカルシウムを有機物等に混入させて土
中で徐々に分解させて発生するガスが、カルシウムと吸
着結合され安定した炭酸カルシウムを得ることができる
家畜糞尿等の再利用法の提供にある。
Means for Solving the Problems The present invention was developed in order to solve the above-mentioned problems, and is a raw material for chemical analysis of cattle dung, pig dung, chicken dung, etc. In a processing method of chemically reacting with electrons and ions after mixing a reactant, a sol-like processing raw material which has been ionized after the chemical reaction is gelated and ammonia (NH 3 ), hydrogen sulfide (H 2 S), trimethylamine A first treatment step for deodorizing a gaseous body such as ((CH 3 ) 3 N) and a foul-smelling substance by the heat generated during the reaction to deodorize;
After the deodorization treatment, CaO (PH13) is 5% of the processing raw material.
Second treatment step in which alkali sterilization is performed with about (weight ratio) additive, and water adsorbed to organic substances and the like after the sterilization treatment is separated from solid content, and further water is extracted to the surface by the action of calcium for dehydration. A third treatment step of: and a fourth treatment of oxidizing the malodorous substance by an oxidizing action gradually volatilized from stable chlorine dioxide (ClO 2 ) after the dehydration treatment to decompose the molecular structure and change it into an odorless molecular structure substance And a fifth treatment step in which the organic treated substance is allowed to stand for a predetermined period after the exhaust deodorization and is cut back at least once during the leaving period to ferment and ripen, and livestock excrement Etc., and the method of storing the processing raw material that temporarily stores organic treated substances such as livestock excrement and supplies them to the feeder in a fixed amount, and temporarily stores calcium oxide (CaO). And a method of supplying calcium oxide in which a constant amount of calcium oxide is supplied to the supply device with respect to the supply amount of the supply device, and the organic treatment substance and calcium oxide are charged into a stirring reaction tank and mixed in the presence of water. A stirring reaction method of reacting, a method of fermenting and aging the organic waste discharged from the stirring reaction tank through a yard and a turning machine that is left for a predetermined time, and a method of treating livestock excrement, etc. In offer. Furthermore, the organic treated substance obtained by the treatment method is a neutralizing action for acidic soil, promotion of fertilizing efficiency of nitrogen, phosphate, potassium, etc., prevention of chlorophyll deficiency and yellowing, effective microorganisms and bacterial cell groups. The purpose of the present invention is to provide a method for reusing livestock excrement, which is characterized by being capable of promoting reproduction, retaining and releasing water (self-absorbing and releasing water, etc.), and reusing it as an organic fertilizer and soil conditioner. Tetravirol, which is a component, is stabilized in the inner core of triple capsules of organic hydroxide, calcium bicarbonate, and calcium carbonate, and gas generated by gradually decomposing in the soil by mixing ultrafine particles of calcium with organic substances etc. The present invention provides a method for reusing livestock excrement and the like, which can obtain stable calcium carbonate by being adsorbed and bound to calcium.

【0006】[0006]

【発明の実施の形態】まず、牛糞、豚糞、鶏糞の家畜糞
尿等を化学分析した処理原料に酸化カルシウム等の反応
剤を混入した後に電子及びイオン作用により化学反応さ
せる処理方法において、前記化学反応後にイオン化され
ているゾル状の処理原料をゲル化しかつアンモニア(N
3 )、硫化水素(H2 S)、トリメチルアミン((C
3 3 N)等のガス体及び悪臭物質を反応時の発熱で
揮散して脱臭させる第1処理工程と、該脱臭処理後にC
aO(PH13)が処理原料の5%(重量比)程度の添
加剤にてアルカリ殺菌させる第2処理工程と、該殺菌処
理後に有機物質等に吸着されている水分を固形分と分離
させ更に水分をカルシウムの働きにより表面に引き出し
て脱水させる第3処理工程と、前記脱水処理後に安定二
酸化塩素(ClO 2 )から徐々に揮散される酸化作用に
より悪臭物質を酸化させて分子構造を分解して無臭の分
子構造物質に変化させる第4処理工程と、前記排気脱臭
後に有機性処理物質を所定期間放置しかつ該放置期間中
に少なくとも1回以上の切り返しをして醗酵熟成させる
第5処理工程とから構成され、更に家畜糞尿等の有機性
処理物質を一時貯溜させて供給機に一定量供給する処理
原料の貯溜方法と、酸化カルシウム(CaO)を一時貯
溜させて前記供給機の供給量に対して酸化カルシウムを
一定量供給機に供給する酸化カルシウムの供給方法と、
前記有機性処理物質及び酸化カルシウムを攪拌反応槽に
投入して水の存在下で混合反応させる攪拌反応方法と、
該攪拌反応槽から排出された有機性廃棄物を所定時間放
置するヤード及び切り返し機を介して醗酵させて熟成さ
せる方法、とから構成されている。
BEST MODE FOR CARRYING OUT THE INVENTION First, livestock manure such as cow dung, pig dung and chicken dung
Reaction of processed oxides such as urine with calcium oxide
After the agent is mixed, it is chemically reacted by the action of electrons and ions.
In the treatment method, the ionization is performed after the chemical reaction.
Gelling the sol-treated raw material that has been discharged and ammonia (N
HThree), Hydrogen sulfide (HTwoS), trimethylamine ((C
HThree) ThreeN) and other gaseous substances and malodorous substances are generated by the heat generated during the reaction.
The first treatment step for deodorizing by volatilizing, and C after the deodorizing treatment
aO (PH13) is about 5% (weight ratio) of the processing raw material.
Second treatment step of alkaline sterilization with an additive, and the sterilization treatment
After adsorption, water adsorbed on organic substances is separated from solids.
Calcium also draws water to the surface by the action of calcium
A third treatment step for dehydration by means of dehydration and a stable treatment after the dehydration treatment.
Chlorine oxide (ClO Two) Is gradually volatilized from
Odorless substances are oxidized and the molecular structure is decomposed
Fourth processing step of changing to child structural material, and the exhaust deodorization
After that, the organic treatment substance is left for a predetermined period and during the left period
Cut at least once more to ferment and mature
It is composed of the fifth treatment step, and is organic such as livestock manure.
Processing to temporarily store the treated substance and to supply a fixed amount to the feeder
Temporary storage of raw material storage method and calcium oxide (CaO)
Accumulate and supply calcium oxide to the supply amount of the feeder.
A method of supplying calcium oxide to be supplied to a constant amount supply machine,
The aforesaid organically treated substance and calcium oxide are placed in a stirring reaction tank.
A stirring reaction method of charging and mixing reaction in the presence of water,
Release the organic waste discharged from the stirring reaction tank for a predetermined time.
Aged by fermenting through a yard to be placed and a turning machine
How to make, and.

【0007】次に再利用方法であるが、前記処理方法に
より得られた有機性処理物質は、酸性土壌の中和作用、
チッソ・リン酸・カリウム等の肥効率の促進、葉緑素の
欠乏及び黄変防止、有効微生物及び菌体群の繁殖助長、
水分の保持及び放出(自己吸放水性等)し、有機肥料及
び土壌改良剤などに再利用でき、更に前記有機肥料の主
成分であるテトラビロールは、有機水酸化塩、重炭酸カ
ルシウム、炭酸カルシウムの三重カプセルの内核に安定
させ、更に超微粒のカルシウムを有機物等に混入させて
土中で徐々に分解されて発生するガスはカルシウムと吸
着結合され安定した炭酸カルシウムを得ることができ
る。
[0007] Next, regarding the recycling method, the organic treated substance obtained by the above treatment method is used for neutralizing the acidic soil,
Promotion of fertilization efficiency of nitrogen, phosphate, potassium, etc., prevention of chlorophyll deficiency and yellowing, promotion of reproduction of effective microorganisms and bacterial groups,
It retains and releases water (self-absorbing and releasing water, etc.) and can be reused for organic fertilizers and soil conditioners. Furthermore, the main component of the organic fertilizer, tetravirol, is composed of organic hydroxide, calcium bicarbonate and calcium carbonate. The gas generated by being stabilized in the inner core of the triple capsule and further being mixed with ultrafine particles of an organic substance to be gradually decomposed in the soil is adsorbed and bound to calcium to obtain stable calcium carbonate.

【0008】[0008]

【実施例】以下、図面に従って本発明の実施例について
説明する。図1は本処理装置のフローシート図であり、
この処理装置1は牛糞、豚糞、鶏糞の家畜糞尿等の有機
性廃棄物2を一時貯溜すると共に定量的に供給する供給
機3を有してなる原料貯留庫4と、酸化カルシウム(C
aO)5を一時貯留すると共に供給機3の供給量に対応
して酸化カルシウム5を定量的に供給する酸化カルシウ
ム供給機6と、有機性廃棄物2及び酸化カルシウム5を
受け入れて水の存在下で混合反応させる攪拌反応槽7
と、この攪拌反応槽7から排出した反応後の有機性廃棄
物2Aを所定時間放置するヤード8及び切返し機9を有
する熟成部10と、からなる。
Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a flow sheet diagram of this processing apparatus.
This processing apparatus 1 temporarily stores organic waste 2 such as cattle dung, pig dung, chicken dung, and the like, and also has a raw material storage 4 having a feeder 3 for quantitatively supplying it, and calcium oxide (C
aO) 5 is temporarily stored and the calcium oxide supplier 6 that quantitatively supplies the calcium oxide 5 corresponding to the supply amount of the supplier 3, and the organic waste 2 and the calcium oxide 5 are received and in the presence of water. Stirring reaction tank 7 for mixing and reacting with
And an aging section 10 having a yard 8 and a turning machine 9 for leaving the reacted organic waste 2A discharged from the stirring reaction tank 7 for a predetermined time.

【0009】前記有機性廃棄物2は、例示のものにのみ
限定されないが、酸化カルシウム5を添加混合すること
により、各種反応を起こし得るものでなければならな
い。前記原料貯留庫4は、ホッパー20の下部に供給機3
を取り付けることで構成される。ホッパー20は、有機性
廃棄物2を一時貯留して供給機3に有機性廃棄物2を安
定して送り、供給機3の供給量に誤差が生じないように
するためのものである。供給機3は、スクリュータイプ
のものが使用されるが、特にこれに限定されず、有機性
廃棄物2を可変して定量的に供給することができるもの
であれば、いかなるものであっても良い。この実施例で
は、スクリューの回転速度を変えることにより有機性廃
棄物2の供給量を可変するものである。
The organic waste 2 is not limited to the exemplified ones, but it must be capable of causing various reactions by adding and mixing calcium oxide 5. The raw material storage 4 is provided below the hopper 20 with a feeder 3
It is composed by attaching. The hopper 20 is for temporarily storing the organic waste 2 and stably sending the organic waste 2 to the feeder 3 so that an error does not occur in the supply amount of the feeder 3. The feeder 3 is of a screw type, but is not particularly limited thereto, and may be of any type as long as the organic waste 2 can be variably and quantitatively supplied. good. In this embodiment, the supply amount of the organic waste 2 is changed by changing the rotation speed of the screw.

【0010】前記酸化カルシウム供給機6は、ホッパー
30の下部に定量供給機31を取り付けることで構成され
る。ホッパー30はほぼ密封され、更に充分な防湿対策を
施されたものである。更に、定量供給機31はスクリュー
タイプやテーブルタイプのものが使用されるが、これに
限定されず、有機性廃棄物2の供給量に合せて設定した
比率で酸化カルシウム5を可変して定量的に供給するこ
とができるものであれば、いかなるものであっても良
い。
The calcium oxide feeder 6 is a hopper
It is configured by attaching a fixed quantity feeder 31 to the lower part of 30. The hopper 30 is almost hermetically sealed and is provided with sufficient moisture-proof measures. Further, although the screw feeder or the table feeder is used as the quantitative feeder 31, the quantitative feeder is not limited to this, and the calcium oxide 5 can be quantitatively changed by varying the calcium oxide 5 at a ratio set according to the supply amount of the organic waste 2. Any material that can be supplied to

【0011】前記攪拌反応槽7は、原料貯留庫4から供
給された有機性廃棄物2及び酸化カルシウム供給機6か
ら供給された酸化カルシウム5を、一旦受け入れる原料
受入ホッパー40を有している。この原料受入ホッパー40
下部には原料投入装置41が設けられ、この原料投入装置
41には、相互に逆方向のスクリュー42、43が同一の軸44
に固定され、この軸44を同一方向に回転することで左右
に有機性廃棄物2及び酸化カルシウム5からなる原料が
運搬され、供給穴(図示せず)からタンク45内に平均的
に投入されるものである。このタンク45は、シャフト46
に4枚羽根の攪拌翼47を複数設けた攪拌機48を2基設
け、更に散水装置49を2基設けてなる。これら2基の攪
拌機48はその攪拌翼47が千鳥状になるようにタンク45内
に設けられており、更に、散水装置49はパイプ50にノズ
ル51を複数もうけてなる。なお、2基の攪拌機48は、可
変減速機付のモータ(図示せず)により回転され、更に
散水装置49は、給水源52から受水槽53にて受けた水を水
圧ポンプ54により増圧してなるものである。従って、原
料投入装置41によりタンク45内に平均的に投入された原
料は、タンク45内で所定時間、例えば7〜15分ほど滞留
して必要に応じて散水装置49により水を散布され、更に
2基の攪拌機48により混合させ、その過程で種々の化学
反応が行なわれ、殺菌消臭等がなされて無害化される。
The stirring reaction tank 7 has a raw material receiving hopper 40 for temporarily receiving the organic waste 2 supplied from the raw material storage 4 and the calcium oxide 5 supplied from the calcium oxide feeder 6. This raw material receiving hopper 40
A raw material feeding device 41 is provided in the lower part.
41 has screws 42, 43 in opposite
By rotating the shaft 44 in the same direction, the raw material composed of the organic waste 2 and the calcium oxide 5 is conveyed to the left and right, and is fed into the tank 45 from the supply hole (not shown) on average. It is something. This tank 45 has a shaft 46
Two agitators 48 each having a plurality of four-bladed agitating blades 47 are provided, and two water sprinklers 49 are further provided. These two stirrers 48 are provided in the tank 45 so that the stirring blades 47 are staggered, and the sprinkler 49 is provided with a pipe 50 and a plurality of nozzles 51. The two agitators 48 are rotated by a motor (not shown) equipped with a variable speed reducer, and the water sprinkler 49 further increases pressure of water received from the water supply source 52 in the water receiving tank 53 by the water pressure pump 54. It will be. Therefore, the raw material charged into the tank 45 on average by the raw material charging device 41 stays in the tank 45 for a predetermined time, for example, about 7 to 15 minutes, and is sprayed with water by the sprinkling device 49 as necessary. The two agitators 48 are used for mixing, various chemical reactions are carried out in the process, and sterilization and deodorization are carried out to render them harmless.

【0012】前記攪拌反応槽7において混合反応された
あとの有機性廃棄物2Aは、攪拌反応槽7下部に設けた
ゲート(図示せず)からコンベアー60に落下して、この
コンベアー60にて前記熟成部10に送られる。
The organic waste 2A after being mixed and reacted in the stirring reaction tank 7 drops from a gate (not shown) provided in the lower portion of the stirring reaction tank 7 to a conveyor 60, and the conveyor 60 is operated to It is sent to the aging section 10.

【0013】この熟成部10は、ヤード8に所定時間、例
えば、2日〜2週間ぐらい反応後の有機性廃棄物2Aを
放置しておき、その間、少なくとも切返し機9により1
回以上の切り返しを行なうものである。ヤード8はコン
クリート製であり、屋外設置の場合、風雨による影響を
防ぐため屋根が設けられる。切返し機9は、ヤード8上
に放置した反応後の原料を切り返すことができるもので
あれば、その型を問わない。
The aging section 10 allows the organic waste 2A after the reaction to be left in the yard 8 for a predetermined time, for example, for 2 days to 2 weeks, and at least during that time, the organic waste 2A is left in the yard 8 by a turning machine 9.
It is to switch back more than once. The yard 8 is made of concrete, and when installed outdoors, a roof is provided to prevent the effects of wind and rain. The turning machine 9 may be of any type as long as it can cut back the raw material after the reaction that has been left on the yard 8.

【0014】次に、上記構成になる本処理装置1によ
り、その処理方法を説明する。牛糞、豚糞、鶏糞の家畜
糞尿等の有機性廃棄物2を収集車にて集めてストックヤ
ード等まで運搬して置き、直ちにコンベアー等の運搬手
段にて原料貯留庫4のホッパー20に投入し貯留する。ホ
ッパー20の下部ある供給機3にて有機性廃棄物2を一定
量攪拌反応槽7の原料受入ホッパー40に供給する。一
方、酸化カルシウム供給機6のホッパー30にコンテナー
等に入った酸化カルシウム5を投入し、定量供給機31に
て有機性廃棄物2の供給量に合せて設定した比率で酸化
カルシウム5を上記原料受入ホッパー40に供給する。更
に、原料受入ホッパー40の下部にある原料投入装置41に
てタンク45内に上記原料を平均的に投入する。この投入
過程で必要に応じて水圧ポンプ54を作動させて散水装置
49にて原料に水を散布し、2基の攪拌機48にて原料を7
分から15分ほど攪拌滞留させることで、化学反応させ脱
臭、殺菌する。このあとタンク45から反応後の有機性廃
棄物2Aを取り出し、コンベアー60にてヤード8に運搬
し、切返し機9によりならし、かつ所定のインターバル
で原料を切返して熟成させることによって有機肥料等が
得られる。
Next, the processing method of the processing apparatus 1 having the above structure will be described. Organic waste 2 such as livestock manure such as cow dung, pig dung, and chicken dung is collected by a collection vehicle and transported to a stockyard or the like, and immediately put into a hopper 20 of a raw material storage 4 by a transportation means such as a conveyor. Store. A certain amount of the organic waste 2 is supplied to the raw material receiving hopper 40 of the stirring reaction tank 7 by the feeder 3 located below the hopper 20. On the other hand, the calcium oxide 5 contained in a container or the like is put into the hopper 30 of the calcium oxide feeder 6, and the calcium oxide 5 is used as a raw material at a ratio set according to the amount of the organic waste 2 fed by the constant quantity feeder 31. Supply to the receiving hopper 40. Furthermore, the above-mentioned raw material is charged into the tank 45 by the raw material charging device 41 below the raw material receiving hopper 40 on average. During this charging process, the water pressure pump 54 is activated as necessary to operate the water sprinkler.
Water is sprinkled on the raw material at 49, and the raw material is mixed by two agitators 48
By stirring and staying for about 15 minutes, a chemical reaction is performed to deodorize and sterilize. After that, the organic waste 2A after the reaction is taken out from the tank 45, transported to the yard 8 by the conveyor 60, leveled by the turning machine 9, and the raw material is turned back at a predetermined interval to be aged, whereby the organic fertilizer or the like is removed. can get.

【0015】図2は有機肥料等の乾燥装置のフローシー
ト図であり、この乾燥機70は主に反応後の有機性廃棄物
2Aの水分値が高い場合に、攪拌反応槽7と熟成部10と
の間に設けられるものである。この乾燥装置70は、コン
ベアー60にて運搬された反応後の有機性廃棄物2Aを投
入タンク71にて受け、この投入タンク71の下部に設けら
れた定量供給機72にてロータリードライヤー本体73の一
端側に投入され、ロータリードライヤー本体73の回転に
より有機性廃棄物2Aは徐々に他端側に移動し、この移
動過程で熱発生炉74からの熱風により乾燥され、一方熱
風は温度を下げつつ、ロータリードライヤー本体73から
排出されて、排ガス処理装置75にて処理され大気中に放
出される。乾燥した有機性廃棄物2Aはロータリードラ
イヤー本体73から排出され、コンベアー76により製品ホ
ッパー77に投入され、必要に応じてホッパーから運搬車
等に移して特殊肥料として使用されるが、上記のように
ヤード8にコンベアー76にて運ばれ、所定時間熟成した
あと有機肥料等として使用される。
FIG. 2 is a flow sheet diagram of a drying apparatus for organic fertilizers, etc. This drying machine 70 is mainly used when the organic waste 2A after the reaction has a high water content, and the stirring reaction tank 7 and the aging section 10 are used. It is provided between and. The drying device 70 receives the organic waste 2A after the reaction carried by the conveyor 60 in a charging tank 71, and a constant quantity feeder 72 provided under the charging tank 71 controls the rotary dryer main body 73 The organic waste 2A is thrown into the one end side, and the organic waste 2A is gradually moved to the other end side by the rotation of the rotary dryer main body 73, and is dried by the hot air from the heat generating furnace 74 in the moving process, while the hot air is lowered in temperature. Is discharged from the rotary dryer main body 73, processed by the exhaust gas processing device 75, and discharged into the atmosphere. The dried organic waste 2A is discharged from the rotary dryer main body 73, put into the product hopper 77 by the conveyor 76, and transferred from the hopper to a transport vehicle or the like for use as a special fertilizer if necessary. It is conveyed to the yard 8 by the conveyor 76 and used as organic fertilizer after aging for a predetermined time.

【0016】なお、図1に示す本処理装置にて製造され
た有機肥料等の分析値を表1に示す。
Table 1 shows the analytical values of the organic fertilizer and the like produced by the present treatment apparatus shown in FIG.

【0017】[0017]

【表1】 [Table 1]

【0018】また、図1に本処理装置の設置場所から5
m離れた位置における臭気濃度の測定値は、表2の数値
を下まわった(なお、濃度測定方法は悪臭防止法に準ず
る。)。
Further, in FIG. 1, 5 from the installation place of this processing apparatus.
The measured value of the odor concentration at a distance of m was below the value in Table 2 (the concentration measurement method is in accordance with the Odor Control Law).

【0019】[0019]

【表2】 [Table 2]

【0020】更に、本処理装置を用いた実験例について
説明する。使用設備 攪拌機:本体、原料投入装置、水分調整装置、反応剤投
入装置、夾雑物除去装置、搬送装置、排気浄化装置、全
自動制御装置(シーケンシャルコントロール方式) 乾燥機:本体、乾燥ハウス、送風・換気装置 付属設備:PH調整装置(乾燥ハウス、送風・換気装
置)、自動計量包装機、成形機、運搬車輌、熱源装置
(廃油バーナー、熱交換器、温風・床暖装置)、面状遠
赤外線発熱装置、排煙洗浄浄化装置 付帯工事:原料貯溜槽、貯水槽、反応剤サイロ、乾燥レ
ーン、原料ヤード、構内舗装工事、建屋(機械室、製品
倉庫、事務所)、電機(一時)・水道(井戸)工事、 本実施例で使用されている攪拌機は、自動計量(ロード
セル方式)された家畜の糞尿と反応剤(生石灰)との化
学反応により悪臭除去・脱水・殺菌・排気脱臭を行い、
低〜高水分の家畜の糞尿を短時間で大量に公害処理を行
なう、また家畜の糞尿及び畜舎の清掃等の汚水は、攪拌
機(反応装置付)で化学反応溶剤(助剤)を使用してい
るので廃水処理施設が不要であり、更にこの装置に家畜
の糞尿を投入した後は化学反応と排気浄化により悪臭は
無くなる。
Further, an experimental example using this processing apparatus will be described. Equipment used Stirrer: Main unit, raw material feeding device, moisture adjusting device, reactant feeding device, contaminant removing device, transfer device, exhaust gas purification device, fully automatic control device (sequential control system) Dryer: main body, drying house, air blower Ventilation equipment Accessory equipment: PH adjustment device (drying house, air blower / ventilator), automatic weighing and packaging machine, molding machine, transport vehicle, heat source device (waste oil burner, heat exchanger, warm air / floor heating device), planar distance Infrared heating device, flue gas cleaning and purification device Additional work: Raw material storage tank, water storage tank, reagent silo, drying lane, raw material yard, yard paving work, building (machine room, product warehouse, office), electric (temporary) The stirrer used in water supply (well) construction and this example is capable of removing offensive odors, dehydration, sterilization, and exhaust deodorization by the chemical reaction between the livestock manure and the reactive agent (quick lime) that are automatically weighed (load cell method). Done,
A large amount of low-to-high-moisture livestock manure is treated in a short period of time, and wastewater such as livestock manure and livestock house cleaning is treated with a chemical reaction solvent (auxiliary agent) using an agitator (with a reaction device). Since no waste water treatment facility is required, the bad odor disappears after the livestock manure is put into this equipment due to chemical reaction and exhaust gas purification.

【0021】また本実施例で使用されている乾燥機は、
全自動無段変速自動畜糞乾燥装置(自然乾燥、ロータリ
ー方式)により約1週間で家畜糞尿の処理物質から有機
肥料等を精製することができる。なお、この乾燥工程の
中では乾燥〜低温醗酵(熟成)が行なわれる。
The dryer used in this embodiment is
An organic fertilizer and the like can be purified from a treated substance of livestock manure in about one week by using a fully automatic continuously variable automatic livestock dung drying device (natural drying, rotary system). In this drying step, drying to low temperature fermentation (aging) is performed.

【0022】処理物質 ア、家畜の糞尿(搾乳牛、肥育牛、養豚、採卵鶏) イ、畜舎の清掃汚水 ウ、屠殺場の血糊、内臓物、廃水濾渦物 Treated substances a, livestock manure (milking cattle, fattening cattle, hog raising, hens) a, livestock cleaning sewage c, blood paste from slaughterhouses, offal, wastewater whirlpool

【0023】化学反応 家畜の糞尿に5〜10%の反応剤を加えて化学反応させる
ことによって、悪臭除去、殺菌、脱水、排気脱臭等の公
害処理を行なうことができる。
Chemical reaction By adding 5 to 10% of a reacting agent to manure of livestock and carrying out a chemical reaction, it is possible to carry out pollution treatment such as removal of offensive odors, sterilization, dehydration and exhaust deodorization.

【0024】醗酵熟成 化学反応により公害処理された家畜の糞尿は、約1週間
の乾燥〜低温醗酵(熟成)工程で含水率35%前後の使い
易い有機肥料等に精製加工することができる。この有機
肥料等を工場の敷地内に野積にしておいても、化学反応
により安息角が一定に保たれているので、膨潤・流出・
地下浸透、飛散の心配はない。また、化学反応によりア
ルカリ処理(殺菌)されているので、製品倉庫や工場敷
地内ではハエ、ウジ虫等の発生も無く衛生的である。
The manure of livestock, which has been pollution-treated by a fermentation aging chemical reaction, can be purified and processed into an easy-to-use organic fertilizer having a water content of about 35% in a drying to low temperature fermentation (aging) process for about 1 week. Even if these organic fertilizers are piled up on the premises of the factory, the angle of repose is kept constant by the chemical reaction, so swelling, outflow,
There is no concern about underground penetration and scattering. Moreover, since it is alkali-treated (sterilized) by a chemical reaction, it is hygienic without the generation of flies, maggots, etc. in the product warehouse and factory premises.

【0025】処理物質(有機肥料等) ア、カルシウムを含んでいるので、酸性土壌の中和作用
としての効果がある。 イ、有機物とカルシウムとの化合物が長時間に亘る施肥
効率が高められる。 ウ、肥料の三要素と、微量成分とがバランスよく含んで
いる。 エ、有機肥料で疲弊した田畑の地力を高めて土壌の活性
化がはかられる。 オ、質量ともに優れた安全性の高い有機質野菜、米、果
物の栽培が容易になる。 カ、悪臭、地下浸透、膨潤、流出、飛散等の心配がな
い。 キ、公害問題で周辺地域の住民に迷惑をかけることがな
い。
Treated substance (organic fertilizer, etc.) (a) Since it contains calcium, it has an effect of neutralizing acidic soil. B. The fertilization efficiency of the compound of organic matter and calcium for a long time is enhanced. C) The three elements of fertilizer and trace elements are contained in a good balance. Oh, soil activation can be promoted by increasing the soil fertility of fields that have been exhausted by organic fertilizers. Easily cultivates organic vegetables, rice, and fruits with excellent e and mass and high safety. There is no concern about mosquitoes, foul odor, underground penetration, swelling, runoff, and scattering. The pollution problem does not cause inconvenience to residents in the surrounding area.

【0026】肥料特性 ア、土壌中に有機微生物(R、ルブラン菌)を培養させ
て土壌を活性化できる。 イ、有機物質を土壌中に貯えることができるので、陽イ
オン交換容量が増大となって保肥力が良くなる。 ウ、塩基類の不足が補って土壌PHの中和を維持できる
ので、土壌の団粒化が促進できる。 エ、集落や根腐れ等が軽減できるので、収穫期間を長く
することが可能となる。 オ、根コブセンチュウや土壌有害菌による嫌地減少を軽
減できるので、増収、増益が可能になる。 カ、カルシウム、ビタミン、ミネラスを多量に含む高品
質の作物ができる。
Fertilizer characteristics a. The soil can be activated by culturing organic microorganisms (R, Leblanc bacteria) in the soil. B. Since organic substances can be stored in the soil, the cation exchange capacity is increased and the fertilizing capacity is improved. C. Since the lack of bases can be compensated and the neutralization of soil PH can be maintained, soil aggregation can be promoted. D. It can reduce crops, root rot, etc., so that the harvest period can be extended. (E) The reduction of unfavorable land caused by root-knot nematodes and soil harmful bacteria can be reduced, so that sales and profits can be increased. It produces high-quality crops containing a large amount of mosquitoes, calcium, vitamins, and Mineras.

【0027】化学原理 ア、化学反応としては、イオン化しているゾル状をゲル
化する。 2(CH3 SH)+CaO→(CH3 S)2 Ca+H2
O 2(RCOOH)+CaO→(R−COO)2 Ca+H
2 O 2(R−NH2 )+CaO→(R−NH2 2 Ca+H
2 O−S−2CaO→CaS イ、揮散としては、アンモニア(NH3 )、硫化水素
(H2 S)、トリメチルアミン((CH3 3 N)等の
ガス体または悪臭物質は、反応時の発熱でも揮散する。
また処理時の処理物残臭気は、空気(O)との接触によ
り窒素ガスとなり無臭となる。 ウ、物理的な要因としては、図3のように電子構成によ
る構造の粒団がすみやかに造成され、Ca(OH)2
Ca(HCO3 2 、CaCO3 が微粒子の細孔の中に
吸着され臭気の拡散がなくなる。 エ、二次反応としては、処理物は空気に接触してすみや
かにカルシウム塩の生成が始まり、また処理物がアルカ
リであることにより空気に接触して腐敗による悪臭は無
くなる。 オ、殺菌としては、アルカリにて殺菌をするがCaO
(PH13)がPHを上げるのではなく、Ca(HCO
3 2 を生成させてアルカリ殺菌をするため投入物のP
Hが6.0〜6.3の物性であっても、投入物がわずか
5%(重量比)の添加剤使用でも完全殺菌を可能にす
る。 カ、脱水としては、図4に示すように有機物質等に吸着
された水分が電子移動により固形分と分離し、水分はカ
ルシウムの働きにより表面に引き出されるので乾燥が早
くなる。なお、処理物は4つの脱臭理由により水分を多
く残して処理しても悪臭を防ぎ、更に7の殺菌理由によ
りハエ、ウジ等の生成の発生を防止することができる。 キ、排気脱臭としては、処理時に発生する排気の臭気は
安定二酸化塩素(ClO 2 )から徐々に揮散される酸化
作用により、悪臭物質を酸化してその分子構造を分解
(破壊)し、無臭の分子構造物質に変化させることがで
きる。ClO2 の悪臭物質との反応は、基本的にはCl
2 →ClO+O(発生期の酸素)が反応できるOの強
い酸化作用による。
[0027]Chemical principle As a chemical reaction, gel the ionized sol
Become 2 (CHThreeSH) + CaO → (CHThreeS)TwoCa + HTwo
O 2 (RCOOH) + CaO → (R-COO)TwoCa + H
TwoO 2 (R-NHTwo) + CaO → (R-NHTwo)TwoCa + H
TwoO-S-2CaO-> CaS IThree), Hydrogen sulfide
(HTwoS), trimethylamine ((CHThree)ThreeN) etc.
Gaseous substances or odorous substances are volatilized even when the heat generated during the reaction.
Also, the residual odor of the processed material during processing is due to contact with air (O).
It becomes nitrogen gas and becomes odorless. C. As for the physical factor, it depends on the electronic configuration as shown in FIG.
Aggregates with a structure that quickly creates Ca (OH)Two,
Ca (HCOThree)Two, CaCOThreeIn the pores of the particles
It is adsorbed and the diffusion of odor disappears. D) As a secondary reaction, the treated product may come into contact with air
The formation of crab calcium salt begins
Because it is in contact with the air, there is no bad odor due to decay.
It becomes. For sterilization, CaO is used for sterilization, but CaO
(PH13) does not raise PH, but Ca (HCO
Three)TwoTo generate P and to sterilize with alkali
Even if H has a physical property of 6.0 to 6.3, the amount of input is small.
Complete sterilization is possible even with the use of 5% (weight ratio) additive.
You. For mosquito and dehydration, as shown in Fig. 4, adsorption to organic substances, etc.
The generated water is separated from the solid content by electron transfer, and the water content
Due to the action of lucium, it is pulled out to the surface so it dries quickly.
It becomes. The treated product contains a lot of water for four reasons.
Even if left untreated, the odor is prevented, and for the reason of 7 sterilization,
It is possible to prevent the generation of flies and maggots. For exhaust deodorization, the odor of exhaust generated during processing is
Stable chlorine dioxide (ClO Two) Is gradually volatilized from
By action, oxidize malodorous substances and decompose their molecular structure
It can be destroyed (destructed) and transformed into an odorless molecular structure substance.
Wear. ClOTwoThe reaction with the malodorous substance is basically Cl
OTwo→ ClO + O (oxygen in nascent stage) can react
Due to the oxidation effect.

【0028】[0028]

【発明の効果】本発明は、牛糞、豚糞、鶏糞等の家畜糞
尿を化学分析した処理原料に酸化カルシウム等の反応剤
を混入した後に電子及びイオン作用により化学反応させ
る処理方法において、前記化学反応後にイオン化されて
いるゾル状の処理原料をゲル化しかつアンモニア(NH
3 )、硫化水素(H2 S)、トリメチルアミン((CH
3 3 N)等のガス体及び悪臭物質を反応時の発熱で揮
散して脱臭させる第1処理工程と、該脱臭処理後にCa
O(PH13)が処理原料の5%(重量比)程度の添加
剤にてアルカリ殺菌させる第2処理工程と、該殺菌処理
後に有機物質等に吸着されている水分を固形分と分離さ
せ更に水分をカルシウムの働きにより表面に引き出して
脱水させる第3処理工程と、前記脱水処理後に安定二酸
化塩素(ClO2 )から徐々に揮散される酸化作用によ
り悪臭物質を酸化させて分子構造を分解して無臭の分子
構造物質に変化させる第4処理工程と、前記排気脱臭後
に有機性処理物質を所定期間放置しかつ該放置期間中に
少なくとも1回以上の切り返しをして醗酵熟成させる第
5処理工程とから構成され、更に家畜糞尿等の有機性処
理物質を一時貯溜させて供給機に一定量供給する処理原
料の貯溜方法と、酸化カルシウム(CaO)を一時貯溜
させて前記供給機の供給量に対して酸化カルシウムを一
定量供給機に供給する酸化カルシウムの供給方法と、前
記有機性処理物質及び酸化カルシウムを攪拌反応槽に投
入して水の存在下で混合反応させる攪拌反応方法と、該
攪拌反応槽から排出された有機性廃棄物を所定時間放置
するヤード及び切り返し機を介して醗酵させて熟成させ
る方法、とから構成されているので、従来の醗酵乾燥方
式によって生じていた問題点を解消すると共に、次のよ
うな多くの成分効果を有する処理物質(有機肥料等)を
提供することができる。 ア、カルシウムを含んでいるので、酸性土壌の中和作用
としての効果がある。 イ、有機物とカルシウムとの化合物の長時間に亘る施肥
効率が高められる。 ウ、肥料の三要素と、微量成分とがバランスよく含んで
いる。 エ、有機肥料で疲弊した田畑の地力を高めて土壌の活性
化がはかられる。 オ、質量ともに優れた安全性の高い有機質野菜、米、果
物の栽培が容易になる。 カ、悪臭、地下浸透、膨潤、流出、飛散等の心配がな
い。 キ、公害問題で周辺地域の住民に迷惑をかけることがな
い。
INDUSTRIAL APPLICABILITY The present invention provides livestock feces such as cow dung, pig dung, and chicken dung.
Reactants such as calcium oxide are used as raw materials for chemical analysis of urine
After mixing with the chemical reaction by the action of electrons and ions
In the treatment method according to
Gelling the sol-treated raw material and ammonia (NH
Three), Hydrogen sulfide (HTwoS), trimethylamine ((CH
Three)ThreeN) and other gaseous substances and malodorous substances are volatilized by the heat generated during the reaction.
The first treatment step for deodorizing by scattering, and Ca after the deodorizing treatment.
O (PH13) is added at about 5% (weight ratio) of the processing raw material
Second treatment step of alkaline sterilization with an agent, and the sterilization treatment
After that, the water adsorbed on the organic substance is separated from the solid content.
In addition, the water is pulled out to the surface by the function of calcium.
Third treatment step for dehydration and stable diacid after the dehydration treatment
Chlorine chloride (ClOTwo) Is gradually volatilized from
Odorless substances that oxidize malodorous substances and decompose the molecular structure
Fourth treatment step of changing to structural material, and after the exhaust deodorization
And leave the organic treatment substance for a specified period of time and
Fermentation and aging by cutting back at least once
It is composed of 5 treatment steps, and further, organic treatment such as livestock excrement.
Raw material that temporarily stores physical substances and supplies a fixed amount to the feeder
Storage method and temporary storage of calcium oxide (CaO)
To supply calcium oxide to the supply amount of the feeder.
The method of supplying calcium oxide to the quantitative feeder, and
Add organic treated substances and calcium oxide to the stirring reaction tank.
A stirring reaction method of mixing and reacting in the presence of water;
Leave the organic waste discharged from the stirring reaction tank for a predetermined time
Fermented and aged through a yard and a turning machine
The conventional fermentation drying method
In addition to eliminating the problems caused by the formula,
Treated substances (organic fertilizers, etc.) that have many ingredient effects
Can be provided. Oh, it contains calcium, so it neutralizes acid soil.
There is an effect as. Fertilization of a compound of organic matter and calcium for a long time
Efficiency is increased. C. Balanced with the three elements of fertilizer and trace ingredients
I have. D. Activate soil by increasing soil fertility in fields that have been exhausted by organic fertilizer
It can be changed. Highly safe organic vegetables, rice, and fruits with excellent e and mass
It makes it easier to grow things. Do not worry about odor, bad odor, underground penetration, swelling, outflow, scattering, etc.
No. G. Do not disturb residents in the surrounding area due to pollution problems.
No.

【0029】また本発明は、前記処理方法により得られ
た有機性処理物質は、酸性土壌の中和作用、チッソ・リ
ン酸・カリウム等の肥効率の促進、葉緑素の欠乏及び黄
変防止、有効微生物及び菌体群の繁殖助長、水分の保持
及び放出(自己吸放水性等)し、有機肥料及び土壌改良
剤などに再利用でき、更に、前記有機肥料の主成分であ
るテトラビロールは、有機水酸化塩、重炭酸カルシウ
ム、炭酸カルシウムの三重カプセルの内核に安定させ、
更に超微粒のカルシウムを有機物等に混入させて土中で
徐々に分解されて発生するガスが、カルシウムと吸着結
合されて安定した炭酸カルシウムを得ることができるの
で、次のような多くの特性を有する有機肥料が得られ
る。 ア、土壌中に有機微生物(R、ルブラン菌)を培養させ
て土壌を活性化できる。 イ、有機物質を土壌中に貯えることができるので、陽イ
オン交換容量が増大となって保肥力が良くなる。 ウ、塩基類の不足を補って、土壌PHの中和を維持でき
るので、土壌の団粒化が促進できる。 エ、集落や根腐れ等が軽減できるので、収穫期間を長く
することが可能となる。 オ、根コブセンチュウや土壌有害菌による嫌地減少を軽
減できるので、増収、増益が可能になる。 カ、カルシウム、ビタミン、ミネラスを多量に含む高品
質の作物ができる。
Further, the present invention provides that the organically treated substance obtained by the above-mentioned treatment method has a neutralizing effect on acidic soil, promotion of fertilization efficiency of nitrogen, phosphate, potassium, etc., prevention of chlorophyll deficiency and yellowing, and effectiveness. It promotes the reproduction of microorganisms and bacterial groups, retains and releases water (self-absorbing and releasing water, etc.), and can be reused for organic fertilizers and soil conditioners.Furthermore, the main component of the organic fertilizer, tetravirol, is organic water. Stabilize in the inner core of triple capsule of oxide salt, calcium bicarbonate, calcium carbonate,
Furthermore, the gas generated by mixing ultrafine calcium into organic matter and gradually decomposing it in the soil can be adsorbed and bound to calcium to obtain stable calcium carbonate. An organic fertilizer having is obtained. A. Soil can be activated by culturing organic microorganisms (R, Leblanc bacterium) in the soil. B. Since organic substances can be stored in the soil, the cation exchange capacity is increased and the fertilizing capacity is improved. C. Since the lack of bases can be compensated and the neutralization of soil PH can be maintained, soil aggregation can be promoted. D. It can reduce crops, root rot, etc., so that the harvest period can be extended. (E) The reduction of unfavorable land caused by root-knot nematodes and soil harmful bacteria can be reduced, so that sales and profits can be increased. It produces high-quality crops containing a large amount of mosquitoes, calcium, vitamins, and Mineras.

【0030】このような構成から成る本発明には、低水
分から高水分の家畜の糞尿を短時間に大量処理すること
が可能となり、廃水処理施設も一切不要となる。また、
全自動制御システム導入による省力化と諸経費の削減を
図ることができるばかりか、機器・設備はアルカリ処理
により腐蝕が少なく耐久性にも優れ堅固で長持されるの
で、有機肥料の精製ランニングコストが安価となる。更
に悪臭、膨潤、流出、地下浸透、飛散の心配がないの
で、地域住民の生活環境を安全に確保することができ
る。
According to the present invention having such a structure, it is possible to process a large amount of manure of livestock having a low to high water content in a short time, and a wastewater treatment facility is not necessary at all. Also,
Not only can we save labor and reduce various expenses by introducing a fully automatic control system, but since the equipment and facilities are alkali-treated, they are durable, durable and durable. It will be cheaper. Further, since there is no fear of bad smell, swelling, runoff, infiltration underground, and scattering, the living environment of local residents can be secured safely.

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

【図1】本発明処理方法のフローシート図FIG. 1 is a flow sheet diagram of the processing method of the present invention.

【図2】本発明処理工程のフローシート図。FIG. 2 is a flow sheet diagram of the processing steps of the present invention.

【図3】本発明処理原理の化学図式。FIG. 3 is a chemical scheme of the processing principle of the present invention.

【図4】本発明処理原理の化学図式。FIG. 4 is a chemical scheme of the processing principle of the present invention.

【符号の説明】[Explanation of symbols]

1 本処理装置 2 有機性
廃棄物 2A 反応後の有機性廃棄物 3 供給機 4 原料貯留庫 5 酸化カ
ルシウム 6 酸化カルシウム供給機 7 攪拌反
応槽 8 ヤード 9 切返し
機 10 熟成部 70 乾燥機
1 This treatment device 2 Organic waste 2A Organic waste after reaction 3 Feeder 4 Raw material storage 5 Calcium oxide 6 Calcium oxide feeder 7 Stirring reaction tank 8 Yard 9 Cutter 10 Aging unit 70 Dryer

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 牛糞、豚糞、鶏糞の家畜糞尿等を化学分
析した処理原料に酸化カルシウム等の反応剤を混入した
後に電子及びイオン作用により化学反応させる処理方法
において、前記化学反応後にイオン化されているゾル状
の処理原料をゲル化しかつアンモニア(NH3 )、硫化
水素(H2 S)、トリメチルアミン((CH3 3 N)
等のガス体及び悪臭物質を反応時の発熱で揮散して脱臭
させる第1処理工程と、該脱臭処理後にCaO(PH1
3)が処理原料の5%(重量比)程度の添加剤にてアル
カリ殺菌させる第2処理工程と、該殺菌処理後に有機物
質等に吸着されている水分を固形分と分離させ更に水分
をカルシウムの働きにより表面に引き出して脱水させる
第3処理工程と、前記脱水処理後に安定二酸化塩素(C
lO2 )から徐々に揮散される酸化作用により悪臭物質
を酸化させて分子構造を分解して無臭の分子構造物質に
変化させる第4処理工程と、前記排気脱臭後に有機性処
理物質を所定期間放置しかつ該放置期間中に少なくとも
1回以上の切り返しをして醗酵熟成させる第5処理工程
とから構成されることを特徴とする家畜糞尿等の処理
法。
1. A treatment method in which cattle dung, pig dung, chicken dung, etc. are chemically analyzed, and a reaction material such as calcium oxide is mixed with a processing raw material and then chemically reacted by an action of electrons and ions, which is ionized after the chemical reaction. Gelling the sol-treated raw material, and ammonia (NH 3 ), hydrogen sulfide (H 2 S), trimethylamine ((CH 3 ) 3 N)
A first treatment step for deodorizing by volatilizing gas bodies and malodorous substances such as the like due to heat generated during the reaction, and CaO (PH1
3) is a second treatment step in which an alkaline sterilization is performed with an additive of about 5% (weight ratio) of the treatment raw material, and water adsorbed on an organic substance or the like after the sterilization treatment is separated from solid content, and water is further calcium. The third treatment step of pulling out to the surface by the function of dehydration and dehydration, and stable chlorine dioxide (C
The fourth treatment step in which the malodorous substance is oxidized by the oxidative action gradually volatilized from 10 O 2 ) to decompose the molecular structure into an odorless molecular structure substance, and the organically treated substance is left for a predetermined period after the exhaust deodorization. And a fifth treatment step of performing fermentation ripening by cutting back at least once during the standing period, and a method for treating livestock excrement and the like.
【請求項2】 家畜糞尿等の有機性処理物質を一時貯溜
させて供給機に一定量供給する処理原料の貯溜方法と、
酸化カルシウム(CaO)を一時貯溜させて前記供給機
の供給量に対して酸化カルシウムを一定量供給機に供給
する酸化カルシウムの供給方法と、前記有機性処理物質
及び酸化カルシウムを攪拌反応槽に投入して水の存在下
で混合反応させる攪拌反応方法と、該攪拌反応槽から排
出された有機性廃棄物を所定時間放置するヤード及び切
り返し機を介して醗酵させて熟成させる方法、とから構
成される請求項1記載の家畜糞尿等の処理法。
2. A method for storing a treated raw material, which temporarily stores an organic treated substance such as livestock excrement and supplies a fixed amount to a feeder,
Calcium oxide (CaO) is temporarily stored to supply a fixed amount of calcium oxide to the supply amount of the supply device, and a method for supplying calcium oxide to the supply device, and the organic treatment substance and calcium oxide are added to a stirring reaction tank. Then, a stirring reaction method of performing a mixed reaction in the presence of water, and a method of fermenting and aging the organic waste discharged from the stirring reaction tank through a yard and a turning machine that are left for a predetermined time, and aging. The method for treating livestock excrement according to claim 1.
【請求項3】 前記処理方法により得られた有機性処理
物質は、酸性土壌の中和作用、チッソ・リン酸・カリウ
ム等の肥効率の促進、葉緑素の欠乏及び黄変防止、有効
微生物及び菌体群の繁殖助長、水分の保持及び放出(自
己吸放水性等)し、有機肥料及び土壌改良剤などに再利
用できることを特徴とする家畜糞尿等の再利用法。
3. The organic treated substance obtained by the treatment method is a neutralizing action of acidic soil, promotion of fertilization efficiency of nitrogen, phosphate, potassium, etc., prevention of chlorophyll deficiency and yellowing, effective microorganisms and fungi. A method for reusing livestock excrement, which is characterized by being capable of promoting the breeding of body groups, retaining and releasing water (self-absorbing and releasing water, etc.), and reusing it as organic fertilizers and soil conditioners.
【請求項4】 前記有機肥料の主成分であるテトラビロ
ールは、有機水酸化塩、重炭酸カルシウム、炭酸カルシ
ウムの三重カプセルの内核に安定させ、更に超微粒のカ
ルシウムを有機物等に混入させて土中で徐々に分解させ
て発生するガスが、カルシウムと吸着結合されて安定し
た炭酸カルシウムを得ることができる請求項3記載の家
畜糞尿等の再利用法。
4. Tetravirol, which is the main component of the organic fertilizer, is stabilized in the inner core of a triple capsule of organic hydroxide, calcium bicarbonate, and calcium carbonate, and ultrafine particles of calcium are mixed with organic matter and the like in the soil. The method for reusing livestock excrement according to claim 3, wherein the gas generated by gradually decomposing in step (3) is adsorbed and bound to calcium to obtain stable calcium carbonate.
JP7309047A 1995-11-28 1995-11-28 Treatment of domestic animal dung and method for recycling the same Pending JPH09142977A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7309047A JPH09142977A (en) 1995-11-28 1995-11-28 Treatment of domestic animal dung and method for recycling the same

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7309047A JPH09142977A (en) 1995-11-28 1995-11-28 Treatment of domestic animal dung and method for recycling the same

Publications (1)

Publication Number Publication Date
JPH09142977A true JPH09142977A (en) 1997-06-03

Family

ID=17988240

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7309047A Pending JPH09142977A (en) 1995-11-28 1995-11-28 Treatment of domestic animal dung and method for recycling the same

Country Status (1)

Country Link
JP (1) JPH09142977A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR102005199B1 (en) * 2018-12-27 2019-07-29 배석훈 Waste water purification and odor removal composition
CN112174476A (en) * 2020-09-25 2021-01-05 广州市凯卫莎环保科技有限公司 Treatment process of biomass mud cake
CN112645551A (en) * 2020-11-18 2021-04-13 河南宏景建筑工程有限公司 Community living excrement treatment method

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR102005199B1 (en) * 2018-12-27 2019-07-29 배석훈 Waste water purification and odor removal composition
WO2020138585A1 (en) * 2018-12-27 2020-07-02 배석훈 Composition for wastewater purification and malodor removal
CN112174476A (en) * 2020-09-25 2021-01-05 广州市凯卫莎环保科技有限公司 Treatment process of biomass mud cake
CN112645551A (en) * 2020-11-18 2021-04-13 河南宏景建筑工程有限公司 Community living excrement treatment method

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