JPS5918352B2 - Processing method for processed materials - Google Patents

Processing method for processed materials

Info

Publication number
JPS5918352B2
JPS5918352B2 JP51096968A JP9696876A JPS5918352B2 JP S5918352 B2 JPS5918352 B2 JP S5918352B2 JP 51096968 A JP51096968 A JP 51096968A JP 9696876 A JP9696876 A JP 9696876A JP S5918352 B2 JPS5918352 B2 JP S5918352B2
Authority
JP
Japan
Prior art keywords
pellets
reaction
composting
reaction vessel
treated
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
Application number
JP51096968A
Other languages
Japanese (ja)
Other versions
JPS5327566A (en
Inventor
知男 和田
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
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Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP51096968A priority Critical patent/JPS5918352B2/en
Publication of JPS5327566A publication Critical patent/JPS5327566A/en
Publication of JPS5918352B2 publication Critical patent/JPS5918352B2/en
Expired 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

Landscapes

  • Filling Or Emptying Of Bunkers, Hoppers, And Tanks (AREA)
  • Treatment Of Sludge (AREA)
  • Fertilizers (AREA)

Description

【発明の詳細な説明】 本発明は家畜ふん尿や下水汚泥等の処理方法及び処理装
置に係り、鳥獣類特に鶏、牛、豚などの家畜類のふん尿
(場合によっては尿はわずか含まれるだけで、実質的に
ふんの処理のこともある)や下水処理場から発生する下
水汚泥や、その他魚介滓や家禽類の死体、凍原、各種有
機性の産業廃棄物等の或は堆肥化処理を行なう場合に係
る処理方法と装置である。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method and apparatus for treating livestock manure, sewage sludge, etc. , sewage sludge generated from sewage treatment plants, other fish dregs, poultry carcasses, frozen fields, various organic industrial wastes, etc., or composting. This is a processing method and apparatus related to the case.

家畜ふん尿などを中心とする上記各種廃棄物は、再利用
可能な形に処理して肥料や飼料などとして再利用するこ
とが望ましい。
It is desirable that the above-mentioned various wastes, mainly livestock manure, be processed into a reusable form and reused as fertilizer, feed, etc.

そのためには、堆肥化処理、が最も好ましいものであり
、この処理の結果、被処理物である家畜ふん尿等は堆肥
になり、肥料等に再利用できるようになる。
For this purpose, composting is the most preferable treatment, and as a result of this treatment, the material to be treated, such as livestock manure, becomes compost, which can be reused as fertilizer.

家畜ふん尿等の堆肥化に際して処理対象物を好気性の適
正な環境条件に保持することが必要で、そのファクター
としては温度、被処理物の含水率、風量、酸素量、或は
処理時間等が重要である。
When composting livestock manure, etc., it is necessary to maintain the material to be treated in appropriate aerobic environmental conditions, and the factors include temperature, moisture content of the material, air volume, oxygen content, and processing time. is important.

すなわち、堆肥化方法の一般的形態を述べるならまず、
堆肥化反応を開始させるには被処理物を適正な含水率(
およそ20−70重量%)に調整し、これを反応容器に
投入して多くの場合強制的に送風して酸素をおくりこみ
好気性とし、自然発生的におこる好気性微生物反応の結
果、被処理物の温度は上昇し、反応が良好ならば、50
℃から80℃にまで上昇するものであり、かつ、この高
温を長時間(多くは24〜48時間)保つことによって
望ましい堆肥を得るものである。
In other words, if we are to describe the general form of the composting method, first of all,
To start the composting reaction, the material to be treated must have an appropriate moisture content (
This is adjusted to approximately 20-70% by weight), then put into a reaction vessel, and in most cases forced air is introduced to bring in oxygen to make it aerobic. As a result of a naturally occurring aerobic microbial reaction, the treated If the temperature of the object increases and the reaction is good, 50
℃ to 80℃, and desired compost can be obtained by maintaining this high temperature for a long time (often 24 to 48 hours).

前述したように、堆肥化反応は家畜ふん尿等の中の有機
質を燃料とし、比較的低温で好気性微生物の介在によっ
て進行する一種の酸化反応であり従って反応の成否は各
種前記ファクターの適正な制御によって左右され、わけ
ても実際面で最も重要になるのは、いかにして反応容器
中の全被処理物に、なるべくむらなく充分な空気を送り
こみ、かつ、そのとき必要なエネルギーを最少におさえ
るかが問題である。
As mentioned above, the composting reaction is a type of oxidation reaction that uses organic matter in livestock manure as fuel and proceeds at a relatively low temperature with the intervention of aerobic microorganisms. Therefore, the success or failure of the reaction depends on appropriate control of the various factors mentioned above. The most important thing in practical terms is how to feed sufficient air as evenly as possible to all the objects to be treated in the reaction vessel, and how to minimize the energy required to do so. is the problem.

従来の堆肥化方法は、いずれもこの点で大きな欠点を有
し、例えば第1図に示すように箱形の反応容器1の底に
メツシュ3を敷き、反応容器1の中に含水率6o%程度
に調整した家畜ふん尿2をそのまま投入し、下から送風
機4等で送風すると被処理物は空気の流通に対して大き
な抵抗を示し従って送風機の馬力数を大きくしなければ
ならない上に、それでもなお矢印で示すように空気は被
処理物の内の反応容器壁に接する附近のみを中心に通過
し、この附近のみが良好な通風状態になるので、中心部
附近はしばしば通風が不充分で嫌便性の状態になり、こ
のため次のような各種の欠点が発生する。
All conventional composting methods have a major drawback in this respect. For example, as shown in FIG. When livestock manure 2 adjusted to a certain level is directly thrown in and air is blown from below with a blower 4, etc., the material to be treated presents a large resistance to the air flow, and therefore the horsepower of the blower must be increased, and even then, As shown by the arrow, air passes only through the area of the object to be processed that is in contact with the reaction vessel wall, and only this area has good ventilation, so the area around the center often has insufficient ventilation and is inconvenient. This leads to various disadvantages such as:

まず、第1に従来のこの方法では充分な堆肥化反応が進
行せず、温度上昇も緩漫となる。
First, in this conventional method, the composting reaction does not proceed sufficiently and the temperature rise becomes slow.

第2に内部の嫌気性反応の結果発生する反応物は肥料と
して危険である。
Second, the reactants generated as a result of internal anaerobic reactions are dangerous as fertilizers.

又第3に通気に必要なエネルギーは大きくこのためラン
ニングコストが大きくなる。
Third, the energy required for ventilation is large, which increases running costs.

本発明は従来の堆肥化方法のこのような欠点を除去する
もので、あらかじめ反応にさきだって被処理物を適正含
水率に調整した後適当な大きさの丸棒上などの形状のペ
レットに成形処理し、しかる後被処理物に強制送風又は
自然送風によってむらなく空気が供給されるように処理
することを特徴とするものである。
The present invention eliminates these drawbacks of conventional composting methods, and involves adjusting the moisture content of the material to be treated at an appropriate level prior to the reaction, and then molding the material into pellets in the shape of a round bar or the like of an appropriate size. The method is characterized in that it is processed so that air is evenly supplied to the object by forced air or natural air.

かくて本発明では、被処理物は丸棒状などの形状のペレ
ットに成形されているので、これを反応容器につめても
常に一つのペレットと他のペレットの間に充分な間隙が
存在し、そこを通って空気が流通するので反応容器全体
にわたって良好な好気性の状態になり、従って全体にわ
たってむらのない充分な堆肥化反応が進行し、温度上昇
も急速におこり、かつ高温になり、又嫌気性反応のおこ
る部分は実質的になくなり、全てが良好な肥料になる上
、通風に必要なエネルギーは極めて少なくて良く、ラン
ニングコストも低下する。
Thus, in the present invention, since the object to be treated is formed into pellets in the shape of a round rod, even when the objects are packed in a reaction container, there is always a sufficient gap between one pellet and another pellet. Since air flows through it, a good aerobic condition is created throughout the reaction vessel, so that a uniform and sufficient composting reaction occurs throughout the vessel, and the temperature rises quickly and becomes high. The part where anaerobic reactions occur is virtually eliminated, and all of it becomes good fertilizer, and the energy required for ventilation is extremely low, reducing running costs.

又全体の反応時間も短くなる。The overall reaction time is also shortened.

次に実施例に基づいて本発明の詳細を述べる。Next, details of the present invention will be described based on examples.

第2図a、bは本発明に係る最も基本的な実施態様で、
図aは反応容器1の側断面図、図すは被処理物を丸棒状
ペレットに成形した場合の被処理物の拡大斜面図である
Figures 2a and 2b show the most basic embodiment of the present invention,
Figure a is a side sectional view of the reaction vessel 1, and the figure is an enlarged perspective view of the object to be treated when it is formed into a round bar-shaped pellet.

図で反応容器壁1は断熱性を考えてアスベスト(石綿)
で作り、(又はエタニットやFRP〜ガラス繊維で補強
したプラスティック等も使用できる)更に外部の補強材
(ここではステイール材)でささえるものでこれは図示
してない。
In the figure, the reaction vessel wall 1 is made of asbestos for insulation.
(or plastic reinforced with eta-knit, FRP, or glass fiber can also be used) and is further supported by an external reinforcing material (steel material here), which is not shown in the drawings.

(低温地域では更に外側に発泡ステイロール板等の断熱
材をあてがうこともある。
(In low-temperature regions, insulation materials such as foam stay roll boards may be applied to the outside.

)反応容器の底部には、約1cn1の間隔でペレットが
落ちない程度のメツシュ3をあてがい、それを更にステ
イールの補強材で補強して用いるのが可である。
) At the bottom of the reaction vessel, it is possible to apply meshes 3 at intervals of about 1cn1 to prevent pellets from falling, and to further reinforce the meshes with steel reinforcing material.

このようにした所にペレット状に成形を施した被処理物
5′を投入し、反応容器1を満たし、次に反応容器1の
下底部から送風機4で送風する。
The object to be treated 5' formed into pellets is put into the thus formed place to fill the reaction vessel 1, and then air is blown from the bottom of the reaction vessel 1 by the blower 4.

ここでは被処理物5′として採卵鶏ふん尿を採用し、こ
れにあらかじめ別な方法で堆肥化と乾燥処理を施してか
ら粉末にした採卵鶏の乾燥堆肥をミキサーで混合し、含
水率50%に調整したのちスクリュープレス式の押出し
成形機(ペレット成形機)を用いて直径30mmの丸棒
状ペレットに成形したが、ペレットの平等長さは7an
位であり、これを前述の反応容器に投入する。
Here, the material to be treated 5' is egg-laying chicken manure, which has been previously composted and dried using a separate method, and then powdered dry compost from egg-laying chickens is mixed in a mixer until the moisture content is 50%. After adjustment, it was molded into round rod-shaped pellets with a diameter of 30 mm using a screw press type extrusion molding machine (pellet molding machine), but the uniform length of the pellets was 7 an.
This is then put into the reaction vessel mentioned above.

反応容器の大きさは、門口3m、奥行3m1高さ4.5
mであり、これに底から3mの高さまでペレットを満た
した。
The size of the reaction container is 3 m at the entrance, 3 m at the depth, and 4.5 m at the height.
m, and was filled with pellets to a height of 3 m from the bottom.

このようにしてから送風機で送風を始めるとまもなく被
処理物は温度上昇を示し、2日で80℃に達した。
As soon as air was started to be blown using a blower, the temperature of the object to be treated increased, reaching 80° C. in two days.

更に送風を続けると、温度はしばらく定常状態を保った
のち、徐々に下降し更に2日後に常温になった。
As the air blowing was continued, the temperature remained steady for a while, then gradually decreased and reached room temperature after two days.

この後ペレットを取り出した所、含水率約30%の良好
な堆肥になっており、かつ、反応容器の内部の方もむら
なく好気性反応を受け、良好な状態を示した。
After this, the pellets were taken out and found to be good compost with a moisture content of about 30%, and the inside of the reaction vessel also underwent an aerobic reaction evenly, indicating good conditions.

第2図すは反応容器内のペレット5′のつまり具合をモ
デル的に示すもので、矢印に示すように、空気はペレッ
ト間のすき間を通って容易に流通する。
Figure 2 is a model showing how the pellets 5' in the reaction vessel are clogged, and air easily flows through the gaps between the pellets as shown by the arrows.

又第3図aは本発明の別の実施態様の反応容器で反応容
器1の下底部に反応後のベレット取出しのための装置と
して回転軸6と爪車7を複数個同図す、cのように設け
たものである。
FIG. 3a shows a reaction vessel according to another embodiment of the present invention, in which a plurality of rotary shafts 6 and ratchet wheels 7 are shown at the bottom of the reaction vessel 1 as a device for taking out pellets after the reaction. It was set up like this.

かくて反応容器1の底部には互いに平行に両端をベアリ
ングで支えた太い回転軸6を複数個通し、前記回転軸6
に第3図すのように複数の爪車7を取りつける。
In this way, a plurality of thick rotating shafts 6 supported by bearings at both ends are passed through the bottom of the reaction vessel 1 parallel to each other, and the rotating shafts 6 are
A plurality of ratchet wheels 7 are attached as shown in Figure 3.

この爪車7は相互にわずかなすき間をもってかみ合い反
応容器1内で処理が行われている際にはペレット5′が
落ちることはない。
The ratchet wheels 7 are engaged with each other with a small gap, so that the pellets 5' do not fall during processing in the reaction vessel 1.

さて、ペレット5′をとりだすには全ての回転軸6の一
端に互にかみ合った歯車(図示せず)をつけ、これの一
つを外部の駆動力で回転すると、第3図aの矢印のよう
に爪車が隣接するものは互いに逆方向に回転し、爪車7
によってペレット51はかき落され回転軸6間のすき間
から下に落ちる。
Now, in order to take out the pellets 5', attach gears (not shown) that mesh with each other to one end of all the rotating shafts 6, and rotate one of them with an external driving force. Adjacent ratchet wheels rotate in opposite directions, and ratchet wheel 7
As a result, the pellets 51 are scraped off and fall down through the gap between the rotating shafts 6.

なお図では爪車7の爪は4枚であるが爪の数を限定する
必要はない。
Although the ratchet wheel 7 has four pawls in the figure, there is no need to limit the number of pawls.

このような回転軸と型車の組合わせは反応容器の底面全
面に広がるようにするのがよいが、下底部の一部にのみ
行われてもよい。
It is preferable that such a combination of the rotating shaft and the mold wheel be spread over the entire bottom surface of the reaction vessel, but it may be formed only on a part of the lower bottom portion.

又第4図は本発明による1実施例処理系統図で、採卵鶏
ふんを例にとって説明すると多くは含水率90%近い半
液状で、これを常温の槽8に貯溜しポンプ9で攪拌して
均質化してから定量ポンプ10で圧送しミキサー11(
スクリュ一式)に一定の割合で送りこむ。
Fig. 4 is a processing system diagram of one embodiment of the present invention. Taking egg-laying chicken manure as an example, most of it is semi-liquid with a water content of nearly 90%. It is stored in a tank 8 at room temperature and stirred with a pump 9 to make it homogeneous. After converting to
(a set of screws) at a constant rate.

ミキサー11には一方からあらかじめ粉末にした乾燥堆
肥12を送りこみ含水率50%になるように混合する。
Dry compost 12, which has been pulverized in advance, is fed into the mixer 11 from one side and mixed to a moisture content of 50%.

この混合物13をペレット成形機14のホッパー14′
へ投入し、片方からスクリュープレスで複数の直径30
關の円形の穴のあいた他端へ向けて押し、それらの穴か
ら混合物を押し出しペレット5′にした。
This mixture 13 is transferred to the hopper 14' of the pellet molding machine 14.
from one side using a screw press to make multiple diameters of 30 mm.
The mixture was pushed toward the other end of the cap which had circular holes, and the mixture was extruded through the holes into pellets 5'.

このペレットをコンベアー15で型車ヲ複数枚底部に有
する反応容器1に投入し、反応容器の下底部より送風機
4で通風して堆肥化したのち底部の型車を回転させてと
りだし、コンベアー(図示せず)で堆肥を再びペレット
成形機14に送りこみ、ペレット化したのち反応容器1
′と同一の乾燥器1に入れ、ヒータ一つきの送風機4′
で温風を送風して含水率18%の乾燥堆肥にした。
The pellets are put into the reaction container 1 which has a plurality of mold wheels at the bottom by a conveyor 15, and are made into compost by ventilation by the blower 4 from the bottom of the reaction container. (not shown), the compost is fed into the pellet forming machine 14 again, and after being pelletized, it is transferred to the reaction vessel 1.
', and a blower with one heater 4'
Hot air was blown to make dry compost with a moisture content of 18%.

更にこれを乾燥器1′の下底部の型車を回転せしめるこ
とによりかき落として取りだし、一部は製品11として
堆積し、一部はハンマーミル18で粉砕して直径約0.
5 mm以下の粉末にしたのちサイロ19に貯溜し、生
ふん尿の含水率調整用に用いる。
Further, this is scraped off by rotating the mold wheel at the bottom of the dryer 1', and a portion is deposited as a product 11, and a portion is crushed by a hammer mill 18 to a diameter of approximately 0.
After grinding into powder of 5 mm or less, it is stored in a silo 19 and used for adjusting the moisture content of raw manure.

なお本発明の実施態様は多岐にわたり、例えば第4図に
示す構成の他に最初の堆肥化はペレット化して行ない、
後の乾燥反応は粉末又は粗粒状のまま行なったり、或い
は反応容器1.乾燥器1′を別個に2つ使うのを止めて
1つの容器とし、被処理物をペレット化して堆肥化反応
をまず完了した後にそのまま温風や常温の空気を強く送
風して乾燥反応に入り、最終製品を作ることもできる。
The embodiments of the present invention are wide-ranging; for example, in addition to the configuration shown in FIG. 4, the initial composting is performed by pelletizing,
The subsequent drying reaction may be carried out in the form of powder or coarse particles, or the reaction vessel 1. Instead of using two separate dryers 1', they are used as one container, and after the material to be treated is pelletized and the composting reaction is first completed, the drying reaction is started by strongly blowing warm air or room temperature air. , can also produce the final product.

或は反応容器ではペレット化して基本的に堆肥。Or, in a reaction vessel, it is turned into pellets and basically composted.

化反応のみを行ない、続いてそこから取り出して、例え
ばビニールハウス、プラスティックハウスやガラス温室
や普通の堆肥舎などの簡便な施設の中において強制通風
なしで(あるいはしても良く、このときは風は乾燥施設
を通ってから堆肥化反応槽に入るようにすると、堆肥が
脱臭作用も持っているので、乾燥施設からの悪臭の発生
を防ぐ)時間をかけて乾燥することもできる。
Only the oxidation reaction is carried out, and then removed from there and placed in a simple facility, such as a vinyl greenhouse, plastic greenhouse, glass greenhouse, or ordinary compost house, without forced ventilation (or without forced ventilation; If the compost passes through a drying facility before entering the composting reaction tank, the compost also has a deodorizing effect, which prevents the generation of bad odors from the drying facility.

あるいは又別の方法として第4図のフローシートにおけ
る乾燥粉末を入れるサイロ19と、ミキサー11とペレ
ット成形機14をまとめて1つのユニットとし、かつ、
しばしばかかるユニットは移動式にし、これと別に第3
図aのような反応容器を複数設け、これらの反応容器は
下から通風できるようにしたのち、前記ユニットを動作
させて成形した被処理物のペレットを1つの反応容器に
満たし、それが終了したら又別の反応容器の所へそのユ
ニットを移動させて同様にしてペレットで反応容器を満
たす。
Alternatively, as another method, the silo 19 containing the dry powder in the flow sheet of FIG. 4, the mixer 11, and the pellet molding machine 14 are combined into one unit, and
Often such units are mobile and have a separate third unit.
After installing a plurality of reaction vessels as shown in Figure a, and making sure that these reaction vessels can be ventilated from below, operate the unit to fill one reaction vessel with pellets of the processed material that have been molded, and then The unit is also moved to another reaction vessel and the reaction vessel is similarly filled with pellets.

このようにして満たされた反応容器において順時通風し
て堆肥化反応と、必要に応じて引き続いて乾燥反応を行
なう。
In the reaction vessel filled in this manner, a composting reaction and, if necessary, a subsequent drying reaction are carried out by sequential ventilation.

このような方法を採用すれば、安価に大容量の処理施設
が建設できる。
If such a method is adopted, a large-capacity treatment facility can be constructed at low cost.

生ふん尿等の被処理の温度が冬期間等で極めて低温であ
ると、堆肥化反応の開始がおくれ、通風機にあわせて補
助熱源を使うことになってランニングコストが増加する
二これをいくらかでも防ぐため熱交換機を前段に設け、
堆肥化槽や乾燥槽から発生する温風を熱源にして被処理
物をあらかじめ加温することは有効である。
If the temperature of raw manure and other materials to be processed is extremely low during winter, etc., the start of the composting reaction will be delayed, and running costs will increase due to the need to use an auxiliary heat source in conjunction with the ventilator. To prevent this, a heat exchanger is installed in the front stage,
It is effective to use warm air generated from a composting tank or a drying tank as a heat source to preheat the material to be processed.

なお投人生ふん尿等の被処理物の水分調整は、わらやお
が屑、もみがら等を用いてもよい。
In addition, straw, sawdust, rice husk, etc. may be used to adjust the moisture content of the material to be treated, such as input manure.

あるいはあらかじめ投入被処理物を他の方法で予め堆肥
化反応に適当に含水率まで乾燥しておくこともあり、も
し得られれば地下熱や温泉や各種廃熱エネルギーがその
源になり、又多くの場合ビニールハウスやプラスティッ
クハウスやガラスハウスを用いて、日光のエネルギーで
予乾することが有効である。
Alternatively, the input material to be treated may be dried in advance to an appropriate moisture content for the composting reaction using other methods. If obtained, underground heat, hot springs, and various waste heat energy can be used as the source, In this case, it is effective to pre-dry using the energy of sunlight using a vinyl house, plastic house, or glass house.

なお堆肥化反応を促進するために、種バクテリアとして
特定の好気性バクテリアを主体にする薬剤をあらかじめ
被処理物に加えることもある。
In order to promote the composting reaction, a chemical containing a specific aerobic bacterium as a seed bacteria may be added to the material in advance.

ペレットの大きさや形に制限はない。There are no restrictions on pellet size or shape.

被処理物を堆肥化反応に先だってペレットに成形する機
械的手段としては、所謂造粒法の内、押出し造粒法又は
圧縮造粒法を用いる。
As a mechanical means for forming the material to be treated into pellets prior to the composting reaction, an extrusion granulation method or a compression granulation method among so-called granulation methods is used.

このうち押出し造粒法は、型(ダイス)に向かって加圧
された被処理物を型の孔から押し出すことによって被処
理物を造粒する方法の総称であり、その実施態様は様々
で制限は無い。
Among these, the extrusion granulation method is a general term for a method of granulating the processed material by extruding the processed material under pressure toward a mold (dice) through the holes of the mold, and there are various implementation methods and limitations. There is no.

つまり1例を示すなら第5図において、ペレット成形機
14′はピストン22にロンド27をかいして油圧シリ
ンダー26をつなぎ、ホッパー20から投入した被処理
物23をチャンバー21内で圧縮し、チャンバーのピス
トンと反対側は複数の丸穴のあいた板24とする。
In other words, to give an example, in FIG. 5, a pellet molding machine 14' connects a hydraulic cylinder 26 to a piston 22 through a rond 27, compresses a workpiece 23 input from a hopper 20 in a chamber 21, and The opposite side of the piston is a plate 24 with a plurality of round holes.

さて油圧でピストン22を穴のあいた板24の方へ押す
と、被処理物は圧縮され、穴から丸棒型のペレット5′
になって落下する。
Now, when the piston 22 is pushed toward the plate 24 with holes using hydraulic pressure, the material to be treated is compressed, and a round bar-shaped pellet 5' is released from the hole.
and fall.

本実施例では穴の直径は18mmから30mmの範囲に
設定した。
In this example, the diameter of the hole was set in the range of 18 mm to 30 mm.

ペレットの長さは押し出し中にペレットが自重で自然に
折れるので、およそ一定(約7cm位)になった。
The length of the pellets was approximately constant (about 7 cm) because the pellets naturally broke under their own weight during extrusion.

押出し造粒法又は圧縮造粒法によって造ったペレットは
充分な機械的強度を持ち、反応容器内において積み重ね
られても相当な堆積高さになるまで上部からの重量によ
って下部のペレットが破壊される事はなく実験によると
反応容器内におけるペレットの最大堆積高さは約7メー
トルであった。
Pellets made by extrusion granulation or compression granulation have sufficient mechanical strength, and even when stacked in a reaction vessel, the lower pellets are destroyed by the weight from the top until a considerable stacking height is reached. According to experiments, the maximum height of pellet accumulation in the reaction vessel was approximately 7 meters.

堆積高さが高い程、装置の占有する床面積は狭くなるの
で好ましい。
The higher the stacking height, the less floor space the apparatus occupies, which is preferable.

一方より簡単な造粒法として、被処理物を高速で回転す
る羽根によって破砕してペレットにする方法もあるが、
この方法により造られたペレットは必要な機械的強度を
持っていないので、反応容器内に積み重ねられると1メ
一トル程度のわずかな堆積高さでも上部からの重量によ
って下部のペレットは破壊されてしまい、従って反応容
器内の空気の流通の妨げとなり、嫌気性反応を起すこと
になるので好ましくない。
On the other hand, a simpler granulation method is to crush the material to be processed into pellets using blades rotating at high speed.
Pellets made by this method do not have the necessary mechanical strength, so when stacked in a reaction vessel, the weight from the top can destroy the bottom pellets even at a small stacking height of about 1 meter. This is undesirable because it obstructs the flow of air within the reaction vessel and causes an anaerobic reaction.

又、反応容器へのペレットの投入方法と取り出し方法に
制限はない。
Furthermore, there are no restrictions on the method of introducing and removing pellets into the reaction vessel.

最も簡単には、反応終了後容器壁の一部をはずし、そこ
からトラクターのフロントローダ−等を挿入してとりだ
す。
The simplest method is to remove a portion of the container wall after the reaction is complete, and insert a front loader of a tractor or the like to take it out.

又送風機は冷風式の他に、電熱式や燃焼式などの温風式
を用い低温時又は多湿時における堆肥化反応や乾燥反応
の遅れを補なうことも可であり、又反応時排気からの悪
臭発生が問題になるなら燃焼式や吸着式等の脱臭装置を
つけることもある。
In addition to the cold air blower, it is also possible to use a hot air blower such as an electric heating type or a combustion type to compensate for delays in composting and drying reactions at low temperatures or high humidity. If the generation of bad odors becomes a problem, a combustion type or adsorption type deodorizing device may be installed.

同様にハンマーミルなどからのチリ、ゴミ発生を防ぐの
に、サイロクン等をつけることもある。
Similarly, to prevent the generation of dust and dirt from hammer mills, etc., a silokun or the like is sometimes installed.

更に本実施例では反応容器を用いているが、反応容器を
用いずに、ペレット化した被処理物を積みあげ開放又は
半開放状態で堆肥化反応を行なうこともある。
Further, although a reaction vessel is used in this embodiment, the pelletized material to be treated may be piled up and the composting reaction may be carried out in an open or semi-open state without using a reaction vessel.

又本発明では被処理物はペレット化されていて極めて通
風性が良好なので場合によっては特別な強制通風なしで
処理を行なうことがある。
Furthermore, in the present invention, the material to be treated is pelletized and has extremely good ventilation, so in some cases the treatment may be carried out without special forced ventilation.

又本発明において被処理物のペレットの堆積に送りこむ
気体は空気の他に、酸素もしくは酸素を含む気体であっ
ても良い。
Further, in the present invention, the gas sent to deposit the pellets of the object to be treated may be oxygen or a gas containing oxygen, in addition to air.

以上本発明の有意性は犬である。The significance of the present invention is dogs.

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

第1図は従来周知の堆肥化方法として用いられる反応容
器の側断面図、第2図aは本発明を説明するための1反
応容器の側断面図、bは被処理物の拡大斜面図、更に第
3図aは本発明に使用される反応容器の1実施例の下底
部を示す側断面図、同図す、cは同下底部の一部の斜面
図、上面図、第4図は本発明による1実施例処理系統図
第5図は被処理物をペレット状に形成する装置の側断面
図である。 図で1は反応容器、5′はペレット状被処理物、6は回
転軸、7は型車。
FIG. 1 is a side sectional view of a reaction container used in a conventionally known composting method, FIG. 2 a is a side sectional view of one reaction container for explaining the present invention, and FIG. Furthermore, FIG. 3a is a side sectional view showing the lower bottom of one embodiment of the reaction vessel used in the present invention, FIG. FIG. 5 is a sectional side view of an apparatus for forming a processed material into pellets. In the figure, 1 is a reaction vessel, 5' is a pellet-like processed material, 6 is a rotating shaft, and 7 is a mold wheel.

Claims (1)

【特許請求の範囲】[Claims] 1 家畜ふん尿や下水汚泥等の有機物を主体とする被処
理物を堆肥化するに際して、堆肥化反応の開始に先立っ
て予め被処理物を機械的造粒手段にてペレット状に造粒
し、該造粒手段が押出し造粒法又は圧縮造粒法に属する
手段であり、更に該ペレットの含水率が20−70重量
%の範囲内にあり、かくて形成された被処理物ペレット
の堆積物に強制送風又は自然送風によって空気のような
酸素を含む気体を送りこみ、好気性微生物を主とする微
生物活動を起させることによって該被処理物を堆肥にす
ることを特徴とする被処理物の処理方法。
1. When composting a material to be treated consisting mainly of organic matter such as livestock manure or sewage sludge, the material to be treated is granulated into pellets using mechanical granulation means prior to the start of the composting reaction. The granulation means belongs to the extrusion granulation method or the compression granulation method, and furthermore, the moisture content of the pellets is within the range of 20 to 70% by weight, and the deposit of the pellets of the processed material thus formed is Processing of a material to be processed, characterized in that the material to be processed is turned into compost by sending a gas containing oxygen such as air through forced or natural ventilation to cause microbial activity, mainly aerobic microorganisms. Method.
JP51096968A 1976-08-16 1976-08-16 Processing method for processed materials Expired JPS5918352B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP51096968A JPS5918352B2 (en) 1976-08-16 1976-08-16 Processing method for processed materials

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP51096968A JPS5918352B2 (en) 1976-08-16 1976-08-16 Processing method for processed materials

Publications (2)

Publication Number Publication Date
JPS5327566A JPS5327566A (en) 1978-03-14
JPS5918352B2 true JPS5918352B2 (en) 1984-04-26

Family

ID=14179019

Family Applications (1)

Application Number Title Priority Date Filing Date
JP51096968A Expired JPS5918352B2 (en) 1976-08-16 1976-08-16 Processing method for processed materials

Country Status (1)

Country Link
JP (1) JPS5918352B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0429478Y2 (en) * 1984-10-23 1992-07-16

Families Citing this family (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5344366A (en) * 1976-10-04 1978-04-21 Tadayuki Yoshida Method of granulating fermentation of organic activated sludges
JPS5667599A (en) * 1979-11-06 1981-06-06 Niigata Eng Co Ltd Treatment for sludge such as waste sand containing organic components
JPS56140096A (en) * 1980-04-01 1981-11-02 Asahi Engineering Organic waste composting method
JPS5855389A (en) * 1981-09-25 1983-04-01 株式会社クボタ Method of composting organic waste
JPS58133896A (en) * 1982-02-01 1983-08-09 Okawara Mfg Co Ltd Composting method of dehydrated sludge
JPS61230797A (en) * 1985-04-05 1986-10-15 Makoto Tomita Method for treating sludge
JPH0322035U (en) * 1989-07-17 1991-03-06
JP4625759B2 (en) * 2005-12-14 2011-02-02 株式会社エムケイ Method and apparatus for automatically carrying treated sludge into a drying container
JP2017067298A (en) * 2014-02-12 2017-04-06 株式会社博石館 Combustion furnace
JP5893670B2 (en) * 2014-05-12 2016-03-23 株式会社森づくり Method for producing dried sludge and treatment method thereof

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0429478Y2 (en) * 1984-10-23 1992-07-16

Also Published As

Publication number Publication date
JPS5327566A (en) 1978-03-14

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