JPS6315040B2 - - Google Patents

Info

Publication number
JPS6315040B2
JPS6315040B2 JP5633380A JP5633380A JPS6315040B2 JP S6315040 B2 JPS6315040 B2 JP S6315040B2 JP 5633380 A JP5633380 A JP 5633380A JP 5633380 A JP5633380 A JP 5633380A JP S6315040 B2 JPS6315040 B2 JP S6315040B2
Authority
JP
Japan
Prior art keywords
fermentation tank
fermenter
livestock manure
heat exchanger
methane
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
JP5633380A
Other languages
Japanese (ja)
Other versions
JPS56152796A (en
Inventor
Tsuneji Hisanaga
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.)
HISANAGA KIKO KK
Original Assignee
HISANAGA KIKO 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 HISANAGA KIKO KK filed Critical HISANAGA KIKO KK
Priority to JP5633380A priority Critical patent/JPS56152796A/en
Publication of JPS56152796A publication Critical patent/JPS56152796A/en
Publication of JPS6315040B2 publication Critical patent/JPS6315040B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Description

【発明の詳細な説明】 本発明は家畜糞処理設備に関するものである。
最近、家畜糞の処理を兼ねて有機肥料を簡便に得
る目的で、家畜糞の堆肥化設備が実用化され、さ
らに堆肥化に先立つて、尿や洗浄水が混入した湿
潤家畜糞を脱水機にて発酵し易い状態にまで脱水
調湿することが行われるようになつたけれども、
脱水調湿処理の際に分離した絞り水汚水によつて
二次公害が生じる。この二次公害を防ぐために絞
り水汚水を無害化処理するには膨大な設備と費用
を要するので、湿潤家畜糞を脱水調湿すると堆肥
化が容易になるという利点があるにもかかわら
ず、湿潤家畜糞の脱水処理の普及が停滞してい
る。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to livestock manure processing equipment.
Recently, composting equipment for livestock manure has been put into practical use in order to process livestock manure and easily obtain organic fertilizer. Furthermore, prior to composting, wet livestock manure mixed with urine and washing water is processed into a dehydrator. However, dehydration and humidity control to a state that facilitates fermentation has become common practice.
Secondary pollution occurs due to wastewater from the squeezing water separated during dehydration and humidity control processing. To prevent this secondary pollution, detoxifying squeezing water wastewater requires a huge amount of equipment and expense. The spread of dehydration treatment for livestock manure is stagnant.

本発明は、絞り水汚水による二次公害を生じる
ことなく、湿潤家畜糞の全量を堆肥化処理する家
畜糞処理設備の提供を目的とするものである。
An object of the present invention is to provide livestock manure processing equipment that composts the entire amount of wet livestock manure without causing secondary pollution due to squeezing water sewage.

本発明の家畜糞処理設備は、湿潤家畜糞を発酵
し易い状態に脱水調湿する脱水機と、脱水調湿し
た家畜糞を二段階にて堆肥化するように竪型一次
発酵槽と横型二次発酵槽とをL字状に連通してな
る発酵槽と、脱水調湿の際に分離した絞り水汚水
をメタン発酵とともに消化するメタン発酵槽とを
備えていて、発酵槽の内部に受熱用熱交換器を配
置し、メタン発酵槽の内部に放熱用熱交換器を配
置し、受熱用熱交換器と放熱用熱交換器とを温水
が循環するように接続し、二次発酵槽から排出さ
れる完熟堆肥の一部を二次発酵槽の始端部に設け
た混合ホツパに返送するとともに、これにメタン
発酵槽から送液管を介して流出する消化液を混合
して二次発酵槽に戻すようになしたことを特徴と
するものである。
The livestock manure processing equipment of the present invention includes a dehydrator that dehydrates and moistens wet livestock manure to a state where it can be easily fermented, a vertical primary fermenter that composts the dehydrated and moistened livestock manure in two stages, and a horizontal two-stage It is equipped with a fermenter that communicates with the next fermenter in an L-shape, and a methane fermenter that digests the squeezing water wastewater separated during dehydration and humidity control with methane fermentation. Place a heat exchanger, place a heat exchanger for heat radiation inside the methane fermentation tank, connect the heat exchanger for heat reception and the heat exchanger for heat radiation so that hot water circulates, and discharge from the secondary fermentation tank. A part of the fully ripened compost is returned to the mixing hopper installed at the starting end of the secondary fermenter, and the digestive juice flowing out from the methane fermenter via the liquid pipe is mixed with this and sent to the secondary fermenter. It is characterized by being made to return to its original state.

以下、本発明を図示の実施例によつて詳細に説
明する。図において、1は湿潤家畜糞Aを発酵し
易い状態に脱水調湿する脱水機であり、2は脱水
調湿家畜糞A1を二段階にて堆肥化する発酵槽で
あり、3は脱水機1によつて分離された絞り水汚
水をメタン発酵とともに消化するメタン発酵槽で
ある。
Hereinafter, the present invention will be explained in detail with reference to illustrated embodiments. In the figure, 1 is a dehydrator that dehydrates and moisturizes wet livestock manure A to a state where it can be easily fermented, 2 is a fermenter that composts the dehydrated and moistened livestock manure A1 in two stages, and 3 is a dehydrator. This is a methane fermentation tank that digests the squeezing water wastewater separated by 1 through methane fermentation.

前記脱水機1は、例えばスクリユー型脱水機で
あつて、ホツパ11に投入された湿潤家畜糞Aを
脱水調湿し、押し出し口12から押し出された脱
水調湿家畜糞A1はコンベヤ13によつて発酵槽
2に投入されるようになつている。他方、脱水調
湿の際に分離した絞り水汚水は多孔部14から流
出し、受皿15、導出管16を経て貯溜槽17内
に溜り、さらに電動機付きポンプ18にて送水管
19を経てメタン発酵槽3に導入されるようにな
つている。
The dehydrator 1 is, for example, a screw type dehydrator, and dehydrates and moisturizes the wet livestock manure A put into the hopper 11, and the dehydrated and moistened livestock manure A1 pushed out from the extrusion port 12 is transferred to the conveyor 13. It is designed to be put into a fermentation tank 2. On the other hand, the squeezing water wastewater separated during dehydration and humidity control flows out from the porous portion 14, passes through the saucer 15 and the outlet pipe 16, accumulates in the storage tank 17, and is further transferred to the water supply pipe 19 by the electric pump 18 for methane fermentation. It is designed to be introduced into tank 3.

前記発酵槽2は調湿家畜糞A1を二段階にて堆
肥化するように竪型一次発酵槽21と横型二次発
酵槽22とをL字状に連通して形成されている。
一次発酵槽21の上方に前記コンベヤ13が臨ん
でいる。一次発酵槽21と二次発酵槽22との断
面形状はともに四角形であり、一次発酵槽21の
容積は1日当り処理する家畜糞の量の10〜15倍の
大きさであり、二次発酵槽22の容積は前記1日
当りの量の9〜14倍の大きさである。23は一次
発酵槽21内において調湿家畜糞の沈降を妨げな
いように垂直に配置した受熱用熱交換器である。
受熱用熱交換器23を二次発酵槽22内にも配置
できることは勿論である。24と25はそれぞれ
二次発酵槽22内に長手方向に沿つて配置した撹
拌移送軸と空気噴出管である。24′は撹拌移送
軸24を駆動する減速器付き電動機である。2
5′はブローワであつて、送気管25″を経て空気
噴出管25から適当量の空気を二次発酵槽22内
に供給するようになつている。26は二次発酵槽
22の始端部に取付けた電動ミキサ付き混合ホツ
パである。二次発酵槽22の終端部に設けたバイ
パス口27から完熟堆肥の一部を取出し、これを
返送完熟堆肥Bとして返送コンベヤ28により混
合ホツパ26に返送し、二次発酵槽22の始端部
に戻すようになつている。
The fermentation tank 2 is formed by connecting a vertical primary fermentation tank 21 and a horizontal secondary fermentation tank 22 in an L-shape so as to compost the humidity-controlled livestock manure A1 in two stages.
The conveyor 13 faces above the primary fermenter 21. Both the primary fermentation tank 21 and the secondary fermentation tank 22 have a rectangular cross-sectional shape, the volume of the primary fermentation tank 21 is 10 to 15 times the amount of livestock manure processed per day, and the secondary fermentation tank The volume of 22 is 9 to 14 times larger than the daily amount. Reference numeral 23 denotes a heat exchanger for receiving heat, which is vertically arranged in the primary fermentation tank 21 so as not to prevent settling of the humidity-controlled livestock manure.
Of course, the heat exchanger 23 for receiving heat can also be placed inside the secondary fermenter 22. Reference numerals 24 and 25 are an agitation transfer shaft and an air jet pipe, respectively, which are arranged along the longitudinal direction within the secondary fermentation tank 22. 24' is an electric motor with a speed reducer that drives the agitation transfer shaft 24. 2
5' is a blower which supplies an appropriate amount of air into the secondary fermentation tank 22 from an air jet pipe 25 through an air supply pipe 25''.26 is a blower at the starting end of the secondary fermentation tank 22. This is a mixing hopper with an attached electric mixer. A part of the ripe compost is taken out from the bypass port 27 provided at the end of the secondary fermentation tank 22, and this is returned to the mixing hopper 26 by the return conveyor 28 as return ripe compost B. , and is returned to the starting end of the secondary fermentation tank 22.

前記メタン発酵槽3は密閉されていて、下部が
汚水溜部で、上部がガス溜部になつている。汚水
溜部の容積は一日当りに生じる絞り水汚水の量の
20〜30倍を収容することができる大きさである。
メタン発酵槽3の外側面には熱の放散を防ぐため
に適宜の保温材を被着してあり、該槽3の天井部
または側面の適当高さの箇所には絞り水汚水を導
入する汚水導入口31を設け、該槽3の底部には
消化液流出口32を設けてある。該槽3内におい
て、槽底の近傍には放熱用熱交換器33を水平に
配置し、その上方には電動機付きミキサ34を配
置し、該槽3の天井部には安全弁35とメタンガ
ス導出管36とを取付けてある。汚水導入口31
は前記送水管19に接続され、消化液は消化液流
出口32から送液管32′を経て該送液管32′の
立上り流出端部から前記電動ミキサ付き混合ホツ
パ26に流出するようになつている。前記消化液
流出口32には送液管32′の立上り流出端部よ
りも低い溢流管を立設してもよい。該溢流路が立
設してあるか、ないかに関係なく、連通管の原理
によつて、メタン発酵槽3内の液面の高さは送液
管32′の流出端部の高さに常に一致するので、
送水管19と汚水導入口31を経てメタン発酵槽
3に導入された絞り水汚水の量と等量の消化液が
消化液流出口32と送液管32′を経て混合ホツ
パ26に自動的に流出するようになつている。3
7は電動機付き循環ポンプであつて、戻り管3
3′と送入管23′とを介して放熱用熱交換器33
と前記受熱用熱交換器23とに温水が循環するよ
うになつている。38は脱硫塔であり、39はメ
タンガスを家庭等に送るメタンガス供給管であ
る。40は脱水機1のホツパ11に湿潤家畜糞A
を投入する投入コンベヤであり、41は二次発酵
槽22の堆肥排出口29から排出される完熟堆肥
A2を搬出する搬出コンベヤである。
The methane fermentation tank 3 is hermetically sealed, with a lower part serving as a sewage reservoir and an upper part serving as a gas reservoir. The volume of the sewage basin is equal to the amount of squeezed wastewater generated per day.
It is large enough to accommodate 20-30 times.
The outer surface of the methane fermentation tank 3 is coated with an appropriate heat insulating material to prevent heat dissipation, and sewage water is introduced into the ceiling or side of the tank 3 at an appropriate height to introduce wastewater from the squeeze water. A mouth 31 is provided, and a digestive fluid outlet 32 is provided at the bottom of the tank 3. In the tank 3, a heat exchanger 33 for heat dissipation is arranged horizontally near the bottom of the tank, a mixer 34 with a motor is arranged above it, and a safety valve 35 and a methane gas outlet pipe are installed in the ceiling of the tank 3. 36 is attached. Sewage inlet 31
is connected to the water supply pipe 19, and the digestive fluid flows from the digestive fluid outlet 32, through the liquid supply pipe 32', and from the rising outflow end of the liquid supply pipe 32' to the mixing hopper 26 with the electric mixer. ing. An overflow pipe may be provided upright at the digestive fluid outflow port 32, which is lower than the rising and outflow end of the liquid sending pipe 32'. Regardless of whether or not the overflow channel is installed upright, due to the principle of the communicating pipe, the liquid level in the methane fermentation tank 3 is equal to the height of the outflow end of the liquid sending pipe 32'. always match, so
Digestive fluid in an amount equal to the amount of squeeze water sewage introduced into the methane fermentation tank 3 via the water supply pipe 19 and the wastewater inlet 31 is automatically transferred to the mixing hopper 26 via the digestive fluid outlet 32 and the liquid supply pipe 32'. It's starting to leak out. 3
7 is a circulation pump with an electric motor, and a return pipe 3
3' and the inlet pipe 23'.
Hot water is circulated between the heat exchanger 23 and the heat receiving heat exchanger 23. 38 is a desulfurization tower, and 39 is a methane gas supply pipe for sending methane gas to homes and the like. 40 is wet livestock manure A in the hopper 11 of the dehydrator 1
41 is an input conveyor for inputting fully ripened compost discharged from the compost discharge port 29 of the secondary fermentation tank 22.
This is an unloading conveyor that unloads A2 .

次に、作用を説明する。まず、畜舎から尿や洗
浄水が混入している湿潤家畜糞Aを猫車等にて搬
出し、投入コンベヤ40にて脱水機1のホツパ1
1に投入すると、圧搾脱水され、発酵し易い状
態、すなわち含水率60〜65%に脱水調湿され、脱
水調湿家畜糞A1になつて押し出し口12から押
し出され、コンベヤ13にて発酵槽2内に投入さ
れる。脱水調湿の際に分離された絞り水汚水は貯
溜槽17に溜まり、ポンプ18にて送水管19を
経てメタン発酵槽3に導入される。発酵槽2に投
入された脱水調湿家畜糞A1は竪型一次発酵槽2
1内を沈降し、次に、横型二次発酵槽22に入
り、撹拌移送軸24によつて撹拌されながら、一
日に二次発酵槽22の長手方向の長さのほぼ1/7
〜1/10に相当する距離だけ送られる。調湿家畜糞
A1は竪型一次発酵槽21を沈降する過程におい
て、発酵して水分を蒸発させ乾燥堆肥になる。横
型二次発酵槽内において、乾燥堆肥は後記するよ
うに返送完熟堆肥Bとともに消化液にて加湿調湿
され、再発酵し、完熟するのである。この際、発
酵槽2の内部を好気的に保たせるために、適当量
の空気をブローワ25′により送気管25″と空気
噴出管25を介して供給する。一次発酵槽21内
に調湿家畜糞A1を投入してから2〜3日後にて
発酵熱が70℃前後に達する。この発酵熱により一
次発酵槽21内に配置した受熱用熱交換器23中
の循環水は50℃程度に加温され、循環ポンプ37
によつて送水管23′を経てメタン発酵槽3内の
放熱用熱交換器33に送入される。メタン発酵槽
3内の絞り水汚水は放熱用熱交換器33により35
℃前後に加温され、20〜30日間かかつて嫌気性の
メタン発酵菌等によつて分解され、メタンガスを
発生するとともに消化され、消化液となる。貯溜
槽17に溜つた絞り水汚水をポンプ18にて適宜
メタン発酵槽3に導入すると、その都度連通管の
原理によつて絞り水汚水の導入量と等量の消化液
が自動的に消化液流出口32から送液管32′を
経て混合ホツパ26内へ流出する。1日にメタン
発酵槽3に導入する絞り水汚水の量は1日の発生
量に相当している。他方、二次発酵槽22のバイ
パス口27から完熟堆肥の一部が返送完熟堆肥B
として返送コンベヤ28にて混合ホツパ26内へ
返送される。混合ホツパ26内において、返送完
熟堆肥Bと消化液との混合、撹拌が行われ、返送
完熟堆肥Bは消化液によつて加湿されたのち、二
次発酵槽22内を撹拌移送軸24によつて徐々に
進行中の一次発酵後の乾燥堆肥に混入される。こ
のことによつて、二次発酵槽22内の乾燥堆肥は
加湿された返送完熟堆肥により適度に調湿される
とともに、返送完熟堆肥B中に多量に含まれてい
る発酵菌によつて種付けされて最適の発酵条件を
保つて再び発酵し、水分を蒸発しながら完熟し、
完熟堆肥になつて堆肥排出口29から排出される
のである。脱水機1にて分離された絞り水汚水は
BOD15000〜20000PPM、固形物濃度6〜8%を
含有するが、メタン発酵槽3内における消化によ
つてBOD3000〜4000PPM程度に低減される。こ
れと同時に、例えば牛の場合には、1日1頭当り
1.12〜1.16m3のメタンガスを発生する。発生した
メタンガスはメタン発酵槽3内の液面上部のガス
溜部に集められ、メタンガス導出管36を経て脱
硫塔38に導入され、硫黄分を除去した後、家庭
用またはエンジン用燃料等に使用されるのであ
る。脱水機1による絞り水汚水をメタン発酵槽3
内において消化させることによつて、メタン発酵
槽3内の汚水上部にスカムが発生しにくい。この
ことによつて、消化液の自動的な流出が円滑に行
われるのである。なお、メタン発酵槽3内に配置
してある電動機付きミキサ34を運転することに
よつて、メタン発酵槽3内の汚水上部にスカムの
発生するのを防ぐとともに、冬期寒冷時にあつて
は、ミキサ34の運転により発生する熱によつて
メタン発酵槽3内の絞り水汚水の加温を助勢する
ことができる。また、メタン発酵槽3に温水を使
用する必要のないときは、送入管23′と戻り管
33′とに取付けてあるバイパス弁にて温水を取
出して洗浄用等に使用することができる。
Next, the effect will be explained. First, wet livestock manure A containing urine and washing water is carried out from the livestock barn using a cat cart, etc., and transferred to the input conveyor 40 into the hopper 1 of the dehydrator 1.
1, it is compressed and dehydrated, dehydrated and moistened to a state that is easy to ferment, that is, with a moisture content of 60 to 65%, turned into dehydrated and moistened livestock manure A1 , and pushed out from the extrusion port 12, and transferred to a fermentation tank by a conveyor 13. It will be put into 2. Squeezed wastewater separated during dehydration and humidity control is collected in a storage tank 17 and introduced into the methane fermentation tank 3 via a water pipe 19 by a pump 18. The dehydrated and humidified livestock manure A1 put into the fermenter 2 is the vertical primary fermenter 2
1, and then enters the horizontal secondary fermentation tank 22, where it is stirred by the agitation transfer shaft 24, and approximately 1/7 of the longitudinal length of the secondary fermentation tank 22 per day.
It is sent by a distance equivalent to ~1/10. Humidity controlled livestock manure
In the process of sedimentation in the vertical primary fermentation tank 21, A1 is fermented and water is evaporated to become dry compost. In the horizontal secondary fermentation tank, the dried compost is humidified together with the returned mature compost B using digestive juices, re-fermented, and fully ripened, as will be described later. At this time, in order to keep the inside of the fermenter 2 aerobic, an appropriate amount of air is supplied by the blower 25' through the air supply pipe 25'' and the air jet pipe 25. Fermentation heat reaches around 70°C 2 to 3 days after livestock manure A 1 is added. Due to this fermentation heat, the circulating water in the heat receiving heat exchanger 23 placed in the primary fermentation tank 21 reaches around 50°C. The circulation pump 37
The water is sent to the heat exchanger 33 for heat radiation inside the methane fermentation tank 3 via the water pipe 23'. Squeezed water and sewage in the methane fermentation tank 3 are removed by a heat exchanger 33 for heat dissipation.
It is heated to around ℃ and decomposed by anaerobic methane-fermenting bacteria for 20 to 30 days, producing methane gas and being digested to become digestive fluid. When the squeezing water wastewater accumulated in the storage tank 17 is appropriately introduced into the methane fermentation tank 3 by the pump 18, the same amount of digestive fluid as the introduced amount of the squeezing water wastewater is automatically added each time according to the principle of the communicating pipe. The liquid flows out from the outlet 32 into the mixing hopper 26 via the liquid feed pipe 32'. The amount of squeeze water wastewater introduced into the methane fermentation tank 3 per day corresponds to the amount generated per day. On the other hand, a part of the ripened compost is returned from the bypass port 27 of the secondary fermentation tank 22 to ripened compost B.
The mixed hopper 26 is returned to the mixing hopper 26 by the return conveyor 28. In the mixing hopper 26, the return ripe compost B and the digestive fluid are mixed and stirred, and the return ripe compost B is humidified by the digestive fluid and then transferred through the secondary fermentation tank 22 by the stirring transfer shaft 24. It is then gradually mixed into the dry compost after primary fermentation, which is in progress. As a result, the dry compost in the secondary fermentation tank 22 is moderately moistened by the humidified returned ripe compost, and is seeded by the fermentation bacteria contained in large quantities in the returned ripe compost B. It is fermented again under optimal fermentation conditions, and the water evaporates until it is fully ripened.
The compost becomes fully ripened and is discharged from the compost outlet 29. The squeezing water wastewater separated in dehydrator 1 is
Although it contains a BOD of 15,000 to 20,000 PPM and a solid concentration of 6 to 8%, it is reduced to about 3,000 to 4,000 PPM by digestion in the methane fermentation tank 3. At the same time, for example, in the case of cows, per head per day.
Generates 1.12-1.16m3 of methane gas. The generated methane gas is collected in the gas reservoir above the liquid level in the methane fermentation tank 3, and introduced into the desulfurization tower 38 via the methane gas outlet pipe 36, where the sulfur content is removed and used as household or engine fuel. It will be done. Squeezed wastewater from dehydrator 1 is transferred to methane fermentation tank 3
By digesting the wastewater inside the methane fermentation tank 3, scum is less likely to be generated in the upper part of the wastewater inside the methane fermentation tank 3. This facilitates automatic outflow of digestive juices. By operating the motorized mixer 34 located inside the methane fermentation tank 3, the generation of scum in the upper part of the sewage inside the methane fermentation tank 3 is prevented, and during cold winters, the mixer 34 is operated. The heat generated by the operation of 34 can assist in heating the squeeze water wastewater in the methane fermentation tank 3. Further, when there is no need to use hot water for the methane fermentation tank 3, the hot water can be taken out by a bypass valve attached to the inlet pipe 23' and the return pipe 33' and used for cleaning or the like.

本発明の家畜糞処理設備によるときは、湿潤家
畜糞を発酵し易い状態に脱水調湿する脱水機と、
脱水調湿した家畜糞を二段階にて堆肥化する発酵
槽と、脱水調湿の際に分離した絞り水汚水をメタ
ン発酵とともに消化するメタン発酵槽とを備えて
いることによつて、絞り水汚水の消化が容易にな
り、発酵槽内における調湿家畜糞の堆肥化処理が
容易になるとともに、堆肥化処理を短時間に完了
することができる。脱水調湿した家畜糞を二段階
にて堆肥化するに当つて、竪型一次発酵槽と横型
二次発酵槽とをL字状に連通して発酵槽を形成し
たものであるので、一次発酵槽内には送込み手段
を設ける必要がなく、構造が簡単になるとともに
発酵槽の設置床面積を縮小することができる。メ
タン発酵槽内において絞り水汚水を消化するもの
であることによつて、メタン発酵槽内にスカムの
発生が少くなり、消化液のメタン発酵槽からの流
出が円滑に行われる。メタン発酵槽内の絞り水汚
水が発酵熱を利用して加温保持するものであるこ
とによつて、消化が促進される。発酵熱を絞り水
汚水の消化に利用するに当つて、発酵槽の内部に
受熱用熱交換器を配置し、メタン発酵槽の内部に
放熱用熱交換器を配置し、受熱用熱交換器と放熱
用熱交換器とを温水が循環できるように接続した
ものであるので、受熱用熱交換器と放熱用熱交換
器等に目詰りを生じることがなく、さらに、メタ
ンガス燃焼装置、温風発生装置等が不要であつ
て、処理設備が単純化されるとともに、保守管理
が容易になるのである。二次発酵槽から排出され
る完熟堆肥の一部を二次発酵槽の始端部に設けた
混合ホツパに返送するとともに、これにメタン発
酵槽から送液管を介して流出する消化液を混合し
て二次発酵槽に戻すようにしたものであるので、
一次発酵後の乾燥堆肥を消化液にて加湿調湿する
とともに返送完熟堆肥による発酵菌の種付けと相
俟つて二次発酵が好条件下に行われ、完熟した堆
肥が得られる。以上のように絞り水汚水による二
次公害を生じることなく、湿潤家畜糞の全量を堆
肥化処理することができるとともに、メタンガス
が得られるのである。
When using the livestock manure processing equipment of the present invention, a dehydrator that dehydrates and adjusts the humidity of wet livestock manure to a state where it is easy to ferment;
By being equipped with a fermenter that composts dehydrated and humidified livestock manure in two stages, and a methane fermentation tank that digests the squeezed water wastewater separated during dehydration and humidification with methane fermentation, Digestion of sewage becomes easier, composting of humidified livestock manure in the fermenter becomes easier, and the composting process can be completed in a short time. In composting dehydrated and moistened livestock manure in two stages, the fermentation tank is formed by connecting a vertical primary fermentation tank and a horizontal secondary fermentation tank in an L-shape, so that the primary fermentation There is no need to provide a feeding means in the tank, which simplifies the structure and reduces the installation floor area of the fermenter. By digesting squeezing water wastewater in the methane fermentation tank, the generation of scum in the methane fermentation tank is reduced, and the digestive fluid flows out smoothly from the methane fermentation tank. Digestion is promoted because the squeezed wastewater in the methane fermentation tank is heated and maintained using fermentation heat. In squeezing the fermentation heat and using it to digest water and sewage, a heat exchanger for heat reception is placed inside the fermenter, a heat exchanger for heat radiation is placed inside the methane fermentation tank, and a heat exchanger for heat reception and a heat exchanger for heat radiation are placed inside the methane fermentation tank. Since the heat exchanger for heat dissipation is connected to allow hot water to circulate, there is no clogging of the heat exchanger for heat reception and heat exchanger for heat dissipation. No equipment is required, the processing equipment is simplified, and maintenance management becomes easier. A portion of the fully ripened compost discharged from the secondary fermenter is returned to the mixing hopper installed at the starting end of the secondary fermenter, and is mixed with the digestive fluid flowing out from the methane fermenter via the liquid pipe. The fermenter is then returned to the secondary fermenter, so
After the primary fermentation, the dry compost is humidified with digestive juices, and the returned ripe compost is used to seed fermentation bacteria. Secondary fermentation is carried out under favorable conditions, and fully ripe compost is obtained. As described above, the entire amount of wet livestock manure can be composted without causing secondary pollution due to waste water from the squeezing water, and methane gas can be obtained.

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

図面は本発明の実施例を示すものであつて、第
1図は家畜糞処理設備全体の配置を示す概略図、
第2図は一部を切断して示す要部の拡大図であ
る。 1:脱水機、2:発酵槽、3:メタン発酵槽、
21:竪型一次発酵槽、22:横型二次発酵槽、
23:受熱用熱交換器、23′:送入管、26:
混合ホツパ、32′:送液管、33:放熱用熱交
換器、33′:戻り管。
The drawings show an embodiment of the present invention, and FIG. 1 is a schematic diagram showing the overall arrangement of livestock manure processing equipment;
FIG. 2 is an enlarged view of the main part, partially cut away. 1: Dehydrator, 2: Fermenter, 3: Methane fermenter,
21: Vertical primary fermenter, 22: Horizontal secondary fermenter,
23: Heat exchanger for heat reception, 23': Inlet pipe, 26:
Mixing hopper, 32': Liquid sending pipe, 33: Heat exchanger for heat radiation, 33': Return pipe.

Claims (1)

【特許請求の範囲】 1 湿潤家畜糞を発酵し易い状態に脱水調湿する
脱水機と、脱水調湿した家畜糞を二段階にて堆肥
化するように竪型一次発酵槽と横型二次発酵槽と
をL字状に連通してなる発酵槽と、脱水調湿の際
に分離した絞り水汚水をメタン発酵とともに消化
するメタン発酵槽とを備えていて、発酵槽の内部
に受熱用熱交換器を配置し、メタン発酵槽の内部
に放熱用熱交換器を配置し、前記受熱用熱交換器
と放熱用熱交換器とを温水が循環するように接続
し、二次発酵槽から排出される完熟堆肥の一部を
二次発酵槽の始端部に設けた混合ホツパに返送す
るとともに、これにメタン発酵槽から送液管を介
して流出する消化液を混合して二次発酵槽に戻す
ようになしたことを特徴とする家畜糞処理設備。 2 脱水機は、スクリユー型脱水機であることを
特徴とする特許請求の範囲第1項記載の家畜糞処
理設備。
[Scope of Claims] 1. A dehydrator that dehydrates and moisturizes wet livestock manure to a state where it can be easily fermented, and a vertical primary fermenter and horizontal secondary fermenter that compost the dehydrated and moistened livestock manure in two stages. It is equipped with a fermentation tank that communicates with the tank in an L-shape, and a methane fermentation tank that digests the squeezing water wastewater separated during dehydration and humidity control with methane fermentation, and a heat exchanger for heat reception inside the fermentation tank. A heat exchanger for heat radiation is placed inside the methane fermentation tank, and the heat exchanger for heat reception and the heat exchanger for heat radiation are connected so that hot water circulates, and hot water is discharged from the secondary fermentation tank. A portion of the fully ripened compost is returned to the mixing hopper installed at the starting end of the secondary fermenter, and the digestive juice flowing out from the methane fermenter via the liquid pipe is mixed with this and returned to the secondary fermenter. Livestock manure processing equipment characterized by the following features: 2. The livestock manure processing equipment according to claim 1, wherein the dehydrator is a screw-type dehydrator.
JP5633380A 1980-04-30 1980-04-30 Method and facility for treating livestock dung Granted JPS56152796A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5633380A JPS56152796A (en) 1980-04-30 1980-04-30 Method and facility for treating livestock dung

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5633380A JPS56152796A (en) 1980-04-30 1980-04-30 Method and facility for treating livestock dung

Publications (2)

Publication Number Publication Date
JPS56152796A JPS56152796A (en) 1981-11-26
JPS6315040B2 true JPS6315040B2 (en) 1988-04-02

Family

ID=13024267

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5633380A Granted JPS56152796A (en) 1980-04-30 1980-04-30 Method and facility for treating livestock dung

Country Status (1)

Country Link
JP (1) JPS56152796A (en)

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS53111303A (en) * 1977-01-07 1978-09-28 Shattock Geoffrey Francis Microbiological treatment

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS53111303A (en) * 1977-01-07 1978-09-28 Shattock Geoffrey Francis Microbiological treatment

Also Published As

Publication number Publication date
JPS56152796A (en) 1981-11-26

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