JPS5950087A - Livestock excrements treatment and device - Google Patents

Livestock excrements treatment and device

Info

Publication number
JPS5950087A
JPS5950087A JP57159638A JP15963882A JPS5950087A JP S5950087 A JPS5950087 A JP S5950087A JP 57159638 A JP57159638 A JP 57159638A JP 15963882 A JP15963882 A JP 15963882A JP S5950087 A JPS5950087 A JP S5950087A
Authority
JP
Japan
Prior art keywords
cylinder
excrement
reaction
manure
quicklime
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.)
Granted
Application number
JP57159638A
Other languages
Japanese (ja)
Other versions
JPS6050756B2 (en
Inventor
福地 盛一
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP57159638A priority Critical patent/JPS6050756B2/en
Publication of JPS5950087A publication Critical patent/JPS5950087A/en
Publication of JPS6050756B2 publication Critical patent/JPS6050756B2/en
Expired 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

  • Fertilizers (AREA)

Abstract

(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。
(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 本発明は、畜糞を生石灰と硝酸を使用して両者の化学反
応に伴う発熱を利用して製品肥料を製造する畜糞処理方
法及びその装置に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a livestock manure processing method and apparatus for producing a product fertilizer by using quicklime and nitric acid from livestock manure and utilizing the heat generated by the chemical reaction between the two.

鶏の糞は約1万羽で毎日1屯の発生があり、大型養鶏場
(100万羽)から小型養鶏場(数千羽)に到るまで、
この糞の処理は企業的にも環境的にも重要関心事となっ
ている。
Approximately 10,000 chickens produce one ton of droppings every day, from large poultry farms (1 million chickens) to small poultry farms (several thousand chickens).
Disposal of this feces is an important concern from both business and environmental perspectives.

一般に、この処理としては糞を火力乾燥して乾燥鶏糞と
して肥料業界に販売していたが、石油価格の高騰により
採算がとれなくなり、これに代る処理として、醗酵促進
剤を添加して堆積自然醗酵を行なわせ堆肥化したり、活
性汚泥方式で浄化水として放流したり、無機薬品を添加
して醗酵を止め半乾状態で肥料化したり等様様な方法で
処理されているのふ現状である。また、牛、豚等につい
ても事情は鶏の事情と全く同様である。種々の処理方法
はめるが、他に敷地、処理台、人件費、製品肥料の品位
価格問題等多くの未解決な問題が残されている。
Generally, this process involved drying the manure over heat and selling it to the fertilizer industry as dried chicken manure, but it became unprofitable due to the soaring oil prices, so an alternative process was to add a fermentation accelerator and sell it to the fertilizer industry. At present, it is treated in a variety of ways, including fermentation and composting, discharging it as purified water using an activated sludge method, and adding inorganic chemicals to stop fermentation and turning it into fertilizer in a semi-dry state. Furthermore, the situation with regard to cows, pigs, etc. is exactly the same as that with chickens. Various treatment methods have been proposed, but many other unresolved issues remain, such as issues regarding site availability, treatment tables, labor costs, and the quality and price of fertilizer products.

本発明による畜糞処理方法及び装置、何時何処ででも入
手容易でありしかも製品肥料としての収入と均衡のとれ
る価格の無機薬品である生石灰と硝酸を使用して、この
両者の化学反応に伴う発熱を利用して、この熱量を完全
に近いまで糞に吸収させて乾燥に必要な熱量を可能なか
ぎり節減して高品位の肥料を製造するものである。
The method and device for treating livestock manure according to the present invention uses quicklime and nitric acid, which are inorganic chemicals that are easily available anytime and anywhere, and whose price is in balance with income as a product fertilizer. By utilizing this amount of heat, the amount of heat required for drying is reduced as much as possible by allowing the dung to almost completely absorb it, thereby producing high-quality fertilizer.

本発明による処理方法を説明すると、入手容易で比較的
に安価でありしかもこれらの添加により肥料としての価
値の向上があるものとして生石灰と硝酸を使用する。こ
れら両者の化学反応熱を糞の含有水の発散に利用する。
To explain the treatment method according to the present invention, quicklime and nitric acid are used because they are easily available and relatively inexpensive, and their addition improves the value as a fertilizer. The heat of chemical reaction between these two is used to release the water contained in the feces.

CaO+2H20=Ca (OHl 2 +H20+ 
15.6000 c alCa(OH12+2HNO,
=Ca(No312+2H,、O+50.600ca/
上記のように生成されたCa(No312すなわち通称
ノルウェー石灰は窒素の施用と同時に石灰が施用される
ので土壌の酸性化を防ぎ、速効性肥料としてこれ自体で
市販されているもので、これと有機遅効性の畜糞と混合
された高品位の肥料を出来る限り省エネルギーで製造す
るの′が本発明による畜糞処理方法である。
CaO+2H20=Ca (OHl 2 +H20+
15.6000 calCa(OH12+2HNO,
=Ca(No312+2H,,O+50.600ca/
Ca (No. 312, commonly known as Norwegian lime) produced as above prevents soil acidification because lime is applied at the same time as nitrogen, and is commercially available on its own as a fast-acting fertilizer. The method of treating livestock manure according to the present invention is to produce high-quality fertilizer mixed with slow-release livestock manure while using as little energy as possible.

本発明による上記処理方法を実施する処理装置を説明す
ると、連続的に送り込まれてくる糞に規定量のCaOを
添加し十分混練した後にHNO3を添加する。逆の順序
で混合することもできるが、糞へ発生反応熱を完全に吸
収するのに難点がある。
To explain the processing apparatus for carrying out the above processing method according to the present invention, a specified amount of CaO is added to continuously fed excrement, and after sufficiently kneading, HNO3 is added. Although it is possible to mix in the reverse order, it is difficult to completely absorb the heat of reaction generated into the feces.

すなわち、HNOうけ強力な酸化作用を持つもので、こ
れは糞と接触すると即座に糞に反応して同時にNOxの
刺戟性のガスが発生して希望の反応の支障となる。それ
故、HNO3の濃度を下げるか、又はHNO3と反応し
ない砂礫土のようなものを添加して解決することもでき
るが、低水分の肥料を製造する場合には水で稀釈するこ
とや異物を混入させることは好ましくない。そこで、本
発明による処理装置によれば、これらの欠点を解消し、
発生反応熱及びガスを完全に糞に吸収させるために、一
部室形の攪拌機を備えた反応筒体すなわち缶に底部より
連続的に糞を圧入し、これに相応する規定量の生石灰C
aOと硝酸HNO3を順次に缶内に連続的に供給し、缶
内で反応を行なわせ、反応熱と同伴するガスを完全に糞
に吸収させる。更に、化学反応熱のみでは含有水分の発
散不足のものを大量の外気との機械的な接触により乾燥
させ、低水分の肥料を製造することのできるものである
That is, HNO has a strong oxidizing action, and when it comes into contact with feces, it immediately reacts with the feces and at the same time generates irritating gas of NOx, which hinders the desired reaction. Therefore, the problem can be solved by lowering the concentration of HNO3 or adding something like gravel that does not react with HNO3, but when producing low-moisture fertilizer, it is necessary to dilute it with water or remove foreign substances. It is not preferable to mix them. Therefore, according to the processing device according to the present invention, these drawbacks can be solved,
In order to completely absorb the generated reaction heat and gas into the feces, the feces are continuously pressurized from the bottom into a reaction cylinder or can equipped with a partially chambered stirrer, and a corresponding specified amount of quicklime C is added.
AO and nitric acid HNO3 are sequentially and continuously supplied into the can to cause a reaction within the can, and the reaction heat and accompanying gas are completely absorbed into the feces. Furthermore, it is possible to produce a low-moisture fertilizer by drying fertilizers whose moisture content is insufficiently released by chemical reaction heat alone by mechanical contact with a large amount of outside air.

以下、図面を参照して本発明による処理装置を詳述する
。本発明による畜糞処理装置はシリンダ内に充填された
糞を油圧で圧出させる圧送ポンプ1すなわち圧送装置を
設置している。装置の底部に・ξイブ18を連結したの
は、発生する熱量と同伴する刺戟性のNOxガスを装置
外に漏らすことなく吸収させるためであり、反応部分の
上部には常に糞によって密閉させた状態にしておくこと
が好しいからである。そのために、装置への糞の供給も
装置の底部から圧入させる。運転中、油圧ポンプ1イの
油圧は減圧弁15で任意設定の油圧に調整された油圧が
常に保持されている。図示は油圧ポンプ14の1サイク
ルを終った瞬間を示す。電磁弁16.17の切換りによ
り弁開閉用油圧シリンダ11のロッドが前後進する。糞
用シリンダ16の先端はロッド先端の弁の圧着で弁座と
なるように製作されており、ロッドの前進でシリンダ1
3内の糞は密閉されるAタイマ一時限中に、Aタイマ一
時限で電磁弁17は切換り圧送用シリンダ12のロッド
が前進して糞はパイプ18によって反応装置の底部よシ
圧入される。Bタイマ一時限中に、Bタイマーの時限で
電磁弁16が切換りロッドは復帰し、ホッパー中の糞は
シリンダ13内に吸込まれる吸込不充分でもロッド11
の前進の時に押込まれる。Cタイマ一時限中に、Cタイ
マ一時限で再び電磁弁16.17の繰返し運転を行なう
Hereinafter, the processing apparatus according to the present invention will be described in detail with reference to the drawings. The livestock excrement processing apparatus according to the present invention is equipped with a pressure pump 1, that is, a pressure feeding device that presses out the feces filled in a cylinder using hydraulic pressure. The reason why ξ Eve 18 was connected to the bottom of the device was to absorb the generated heat and the accompanying irritating NOx gas without leaking out of the device, and the top of the reaction part was always sealed with feces. This is because it is preferable to leave it in this state. For this purpose, the supply of feces to the device is also forced into the bottom of the device. During operation, the oil pressure of the hydraulic pump 1a is always maintained at an arbitrarily set oil pressure using the pressure reducing valve 15. The illustration shows the moment when the hydraulic pump 14 completes one cycle. By switching the solenoid valves 16 and 17, the rod of the valve opening/closing hydraulic cylinder 11 moves back and forth. The tip of the excrement cylinder 16 is made to act as a valve seat by crimping the valve at the tip of the rod, and when the rod moves forward, the cylinder 1
During one time period of A timer, the solenoid valve 17 is switched and the rod of the pressure-feeding cylinder 12 moves forward, and the waste is forced into the bottom of the reactor through the pipe 18. . During the B timer's one-time period, the solenoid valve 16 is switched and the rod is returned to its original position, and the feces in the hopper are sucked into the cylinder 13.Even if the suction is insufficient, the rod 11
Pushed in when moving forward. During the C timer's one-time period, the solenoid valves 16 and 17 are operated repeatedly during the C-timer's one-time period.

生石灰供給機3及び硝酸供給機2が設置されており、該
供給機2,3は各々駆動伝動機21゜31の回転制御に
よって行なわれ、いずれも無段変速機付減速機を備えて
いる。硝酸の供給に関して、硝酸は液体であるので、プ
ランジャー型のポンプで圧入され得る。生石灰の供給に
関して、生石灰は微粉のために、送込みスクリュー32
は、反応装置入口部は羽根なしに構成し、生石灰自体で
圧縮密閉し、糞の流入を防ぐ。
A quicklime feeder 3 and a nitric acid feeder 2 are installed, and the feeders 2 and 3 are each controlled by rotation of drive transmissions 21 and 31, and both are equipped with a speed reducer with a continuously variable transmission. Regarding the supply of nitric acid, since nitric acid is a liquid, it can be pressurized with a plunger type pump. Regarding the supply of quicklime, since the quicklime is fine powder, the feed screw 32
The inlet of the reactor is constructed without blades and is compressed and sealed with quicklime itself to prevent the inflow of excrement.

反応装置4は図示のように攪拌翼付きの竪型の筒体41
と水平型の攪拌搬送の筒体44から成る。
As shown in the figure, the reactor 4 has a vertical cylinder body 41 with stirring blades.
and a horizontal stirring conveyance cylinder 44.

圧入される生石灰と硝酸とがそれぞれ単独に糞との反応
を出来るだけ避けるように、糞は筒体1の中央底部から
圧入され、生石灰と硝酸は筒体4の下部側壁部より入れ
られる。まず、これらは遠心翼46で攪拌され、次いで
求心翼42で攪拌され、これらの攪拌を繰返して油圧ポ
ンプでの糞の圧力で逐次に上部へと搬送され寿から反応
を行なわせる。筒体41は発生ガスを糞中に完全に吸収
させるのに十分な高さに設計されており、筒体44で発
熱によって水分の発散を行なう。筒体44内には搬送に
必要な任意角度付きの掻羽根付きの2本の軸45が歯車
伝動によって互に逆転させられており、混練しながら搬
送して水分の発散と反応作用が完結される。筒体44で
は常に既定の水位での混線を行なわせるように排出孔側
に水位保持板46を設け、生成物をこの板46より溢流
させる。
In order to prevent the press-fitted quicklime and nitric acid from reacting individually with the excrement as much as possible, the excrement is press-fitted from the center bottom of the cylinder 1, and the quicklime and nitric acid are introduced from the lower side wall of the cylinder 4. First, these are stirred by the centrifugal blades 46, then by the centripetal blades 42, these stirrings are repeated, and the pressure of the excrement from the hydraulic pump is used to sequentially transport them to the upper part, where they are reacted from the beginning. The cylindrical body 41 is designed to have a height sufficient to completely absorb the generated gas into the excrement, and the cylindrical body 44 evaporates moisture by generating heat. Inside the cylindrical body 44, two shafts 45 with scrapers at arbitrary angles necessary for conveyance are rotated in reverse by gear transmission, and are conveyed while kneading to complete the dispersion of moisture and reaction action. Ru. In the cylindrical body 44, a water level holding plate 46 is provided on the discharge hole side so that crosstalk is always performed at a predetermined water level, and the product overflows from this plate 46.

反応装置4では、熱の吸収、反応の完結及び生成物Ca
(NO,+2と糞との十分な混線等を行たったが、次い
で、水分発散筒体5を設置して、そこで水分の発散促進
を行なわせる。筒体5内には、歯車伝動で互に逆転する
2本の軸に掻上羽根51が取付けられている。筒体44
から落下して生成物はこの羽根で掻上げられ、互に逆転
中の羽根相互間に挾まれ、衝突して脆く疎開し、大部分
は筒体中に浮上の状態で搬送される。一方、排風機57
は外気をこの流れと向流にこの筒体44経出で吸引して
いるので、水分発散の表面積が拡大された生成物は、空
気と充分に接触して、水分発散を行ない、しかも粗砕が
行なわれ、外気を遮断する排出弁56を通じて装置外に
取出される。
In the reactor 4, heat is absorbed, the reaction is completed, and the product Ca
(After sufficient crosstalk between NO, +2 and feces, etc., a moisture dissipating cylinder 5 is installed to promote moisture dissipation there. Scraping blades 51 are attached to the two rotating shafts. Cylindrical body 44
The product falls from the cylinder, is scraped up by the blades, is caught between the blades that are rotating in reverse, collides, and is brittle and evacuated, with most of the product being conveyed into the cylinder in a floating state. On the other hand, the exhaust fan 57
Since the outside air is sucked in through the cylinder 44 in a countercurrent direction to this flow, the product with an expanded surface area for moisture dissipation comes into sufficient contact with the air, wicks moisture, and is finely crushed. is carried out, and is taken out of the apparatus through a discharge valve 56 that shuts off outside air.

経験によれば、水分70%以下の糞の場合には、この装
置の処理によれば、肥料として市販されるときは水分4
5%で好ましいものとなり、化学反応熱のみに依存した
水分の発散でなく、大量の外気との完全表接触による空
気の水分同伴であり、このまま製品となるが、高水分の
糞の場合には筒体5の底部に設置した熱風発生炉52を
点火して不足分の熱を供給する。炉52は耐火物製の燃
焼室であり、ここで発生した完全燃焼ガスは外気取入口
54より吸込まれる大量の空気で稀釈される。
Experience has shown that in the case of manure with a moisture content of less than 70%, the treatment of this device will reduce the moisture content to 4% when marketed as fertilizer.
A value of 5% is preferable, and moisture is not released depending only on the heat of chemical reaction, but moisture is entrained in the air through complete surface contact with a large amount of outside air, and it becomes a product as it is, but in the case of high-moisture feces, A hot air generating furnace 52 installed at the bottom of the cylindrical body 5 is ignited to supply the insufficient heat. The furnace 52 is a combustion chamber made of refractory material, and the complete combustion gas generated here is diluted with a large amount of air sucked in through the outside air intake port 54.

排調機57よりの排ガスは水蒸気と共に悪臭を伴うこと
は糞処理の悩みであるが本装置のものは火力乾燥の如く
高温ガスと糞との接触により発生する臭気は極めて微少
となる。
The exhaust gas from the exhaust conditioner 57 is accompanied by water vapor and a bad odor, which is a problem when treating excrement, but with this device, the odor generated by the contact between high-temperature gas and excrement, as in the case of thermal drying, is extremely small.

次に、本発明による処理の場合の所要熱量と従来の火力
乾燥による処理の場合の所要熱量とを比較する。
Next, the amount of heat required for the treatment according to the present invention and the amount of heat required for the treatment by conventional thermal drying will be compared.

1、 本発明による処理の場合 水分70チの鶏糞11000jcを生石灰1ocucg
と濃度98チの硝酸225に9で処理する。製品肥料は
この処理のものは二次醗酵の心配がないので、製品の水
分は45%で十分であるので、水分45チとして計算す
る。
1. In the case of the treatment according to the present invention, 11000jc of chicken manure with a moisture content of 70g is mixed with 1ocucg of quicklime.
and treated with 225% to 9% nitric acid at a concentration of 98%. Product fertilizers treated in this way do not have to worry about secondary fermentation, so the moisture content of the product is sufficient at 45%, so the moisture content is calculated as 45%.

無水物: 1000xO,3=300 C1cFl)C
ab:         100(にg)HNO3: 
225X0.98=220.5(#1計       
     620.5 (IC91水分45チのもツバ
水5 [17,7k17、無水物620.5kgで、1
.1287cg止りである。
Anhydride: 1000xO, 3=300 C1cFl)C
ab: 100 (g) HNO3:
225X0.98=220.5 (#1 total
620.5 (IC91 moisture 45 cm Motsuba water 5 [17.7k17, anhydrous 620.5kg, 1
.. It is limited to 1287cg.

必要発散水は700−507=193 <Icy+必要
熱量 水蒸発所要熱量550X193=106150(kea
J+充填物が吸収する熱量 り、9X(1000+100+2251X(80−20
)=71550 (kca/1 合計177.700 kca/ 発生熱量 Cao+2HNO5”Ca (No 5 )
 2十H20+66.4 kc aj?66.4X(1
00,0[][]+225.0001/(56十126
 )=118.57D1cca/不足熱量 177.7
00−118.570=59.130kca159、1
30 kca/ は重油換算で約61に和尚する。
Required evaporation water is 700-507 = 193 <Icy + required heat amount Required heat amount for water evaporation 550 x 193 = 106150 (kea
J+ The amount of heat absorbed by the filling, 9X (1000 + 100 + 2251X (80-20
)=71550 (kca/1 Total 177.700 kca/ Generated heat amount Cao+2HNO5”Ca (No 5)
20H20+66.4 kc aj? 66.4X(1
00,0[][]+225.0001/(56126
)=118.57D1cca/deficit calorie 177.7
00-118.570=59.130kca159,1
30 kca/ is equivalent to approximately 61 in terms of heavy oil.

2、火力乾燥による処理の場合 この場合は二次醗酵の恐れがあるので鶏糞を市販されて
いる水分12%に乾燥するものとして計算する。
2. In the case of thermal drying treatment In this case, there is a risk of secondary fermentation, so calculations are made assuming that chicken manure is dried to a commercially available moisture content of 12%.

水分70%の鶏糞1000kg中の無水物は300kg
である。水分12%のものは水41 kg、無水物30
0109で341kg止りである。
There are 300 kg of anhydrous in 1000 kg of chicken manure with 70% moisture content.
It is. The one with 12% moisture content is 41 kg of water and 30 kg of anhydride.
At 0109, it only weighs 341kg.

必要発散水は700−41 =659 (#)である。The required water dissipation is 700-41 = 659 (#).

完全に他より熱を与えての水分発散であり、このために
熱風発生炉の出口温度300℃、乾燥機出口温度120
℃、製品温阪80°0、外気及び糞温20“Cの通風乾
燥機を使用した場合とする。
Moisture is completely released by giving more heat than other parts, and for this purpose, the outlet temperature of the hot air generating furnace is 300℃, and the outlet temperature of the dryer is 120℃.
℃, Product temperature: 80°C, Outside air and feces temperature: 20"C when using a ventilation dryer.

水蒸発所要熱1i(594+120x0.44−20x
659=415.061 kcal! 無水物の加熱所要熱量0.5X300X(80−20+
=5400 kcal! 含有水の加熱所要熱量lX700X(80−201=4
2000 kea/ 稀釈空気の加熱所要熱量(41!1.01!Si+54
00+420001÷(0,24X(300−1201
)Xo、24X(120−201=255.811 小計 716.272 kcal! 熱損失を10チとすると、716.272 X 1.1
 =787、900 (keal!+  787.90
0 kcal! は重油換算で約80!に相当する。
Heat required for water evaporation 1i (594+120x0.44-20x
659=415.061 kcal! Required heat amount for heating anhydride 0.5X300X (80-20+
=5400 kcal! Required heat amount for heating the contained water lX700X (80-201=4
2000 kea/ Required heat amount for heating diluted air (41!1.01!Si+54
00+420001÷(0,24X(300-1201
)
=787,900 (keal!+787.90
0 kcal! is about 80 in terms of heavy oil! corresponds to

以上のように、本発明による処理方法及び装置を用いて
畜糞を処理すれば、重油等を非常に節約することができ
ることは勿論である。
As described above, if livestock manure is treated using the treatment method and apparatus according to the present invention, heavy oil and the like can be greatly saved.

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

第1図は本発明による畜糞処理装置を示す概略断面図、 第2図は第1図の悲Cにおける断面図、第3図は第1図
の線すにおける断面図、第4図は第1図の線aにおける
断面図、第5図は第1図の線dにおける断面図、1・・
・圧送装置    2・・・硝酸供給機6・・・生石灰
供給機  4・・・反応装置5・・・水分発散筒体 42.43,45.51・・・攪拌翼 41・・・竪型の筒体  44・・・水平壓の筒体52
・・・熱風発生炉 代理人 弁理士  戸 1)親 男 第  2  図 第3図 第  5  図
Fig. 1 is a schematic cross-sectional view showing a livestock manure processing apparatus according to the present invention, Fig. 2 is a cross-sectional view taken along line C in Fig. 1, Fig. 3 is a cross-sectional view taken along line C in Fig. 1, and Fig. 4 is a cross-sectional view taken along 5 is a sectional view taken along line a in the figure, and FIG. 5 is a sectional view taken along line d in FIG.
- Pressure feeding device 2... Nitric acid feeder 6... Quicklime feeder 4... Reactor 5... Moisture release cylinder 42.43, 45.51... Stirring blade 41... Vertical type Cylinder 44...Horizontal cylinder 52
...Hot air generator agent Patent attorney 1) Parent Male Figure 2 Figure 3 Figure 5

Claims (2)

【特許請求の範囲】[Claims] (1)密閉状態の筒体内にその底部より糞を圧入する工
程、所定量の生石灰を前記筒体内に入れて混合反応させ
る工程、次いで、所定量の硝酸を前記筒体内に入れて混
合反応させる工程、発生反応熱及びガスを完全に前記糞
に吸収させ、更に大量の外気と機械的に接触させて乾燥
させる工程、から成ることを特徴とする畜糞処理方法。
(1) A step of pressurizing excrement into a sealed cylinder from the bottom, a step of putting a predetermined amount of quicklime into the cylinder and causing a mixing reaction, and then a step of putting a predetermined amount of nitric acid into the cylinder and causing a mixing reaction. A method for treating livestock manure, comprising the steps of: completely absorbing the generated reaction heat and gas into the manure; and further drying the manure by mechanically contacting it with a large amount of outside air.
(2)攪拌翼を備えた竪型の筒体と前記筒体に連結され
かつ攪拌翼を備えた水平型の筒体とから成る反応装置を
備え、前記竪型の筒体の底部に連結されかつ糞を前記筒
体内に圧入する圧送装置及び前記竪型の筒体壁部に連結
されている生石灰供給機及び硝酸供給機が設けられてお
り、更に、前記水平型筒体の下流に設置されかつ攪拌翼
を備えた水分発散筒体が設けられかつ前記水分発散筒体
には熱風発生炉が設けられていることを特徴とする畜糞
処理装置。
(2) A reaction device comprising a vertical cylinder equipped with a stirring blade and a horizontal cylinder connected to the cylinder and equipped with a stirring blade, the reaction device being connected to the bottom of the vertical cylinder. Further, a pressure feeding device for pressurizing excrement into the cylinder, a quicklime feeder and a nitric acid feeder connected to the wall of the vertical cylinder are provided, and a feeder is further provided downstream of the horizontal cylinder. A livestock excrement processing apparatus characterized in that a moisture dissipating cylinder is provided with stirring blades, and a hot air generating furnace is provided in the moisture dissipating cylinder.
JP57159638A 1982-09-16 1982-09-16 Livestock manure processing method and equipment Expired JPS6050756B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57159638A JPS6050756B2 (en) 1982-09-16 1982-09-16 Livestock manure processing method and equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57159638A JPS6050756B2 (en) 1982-09-16 1982-09-16 Livestock manure processing method and equipment

Publications (2)

Publication Number Publication Date
JPS5950087A true JPS5950087A (en) 1984-03-22
JPS6050756B2 JPS6050756B2 (en) 1985-11-09

Family

ID=15698083

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57159638A Expired JPS6050756B2 (en) 1982-09-16 1982-09-16 Livestock manure processing method and equipment

Country Status (1)

Country Link
JP (1) JPS6050756B2 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61183935U (en) * 1985-05-09 1986-11-17
JPH02120289A (en) * 1988-10-28 1990-05-08 Satoshi Inoue Method for composting livestock excreta and bedding mixture and apparatus therefor
CN104817355A (en) * 2015-04-22 2015-08-05 于书强 High-energy thermal fertilizer

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61183935U (en) * 1985-05-09 1986-11-17
JPH0543075Y2 (en) * 1985-05-09 1993-10-29
JPH02120289A (en) * 1988-10-28 1990-05-08 Satoshi Inoue Method for composting livestock excreta and bedding mixture and apparatus therefor
CN104817355A (en) * 2015-04-22 2015-08-05 于书强 High-energy thermal fertilizer

Also Published As

Publication number Publication date
JPS6050756B2 (en) 1985-11-09

Similar Documents

Publication Publication Date Title
US4872998A (en) Apparatus and process for forming uniform, pelletizable sludge product
EP2284129A1 (en) Biomass converters and processes
JP6470744B2 (en) Treatment of organic waste
BRPI0807734A2 (en) PROCESS FOR TREATMENT OF MUD AND MANUFACTURE OF INORGANIC FERTILIZER CONTAINING HIGHLY BIOORGANICALLY RICH NITROGEN
US5259977A (en) Method and apparatus for the treatment of sewage sludge and the like
US4295972A (en) Method for treating water containing wastes
US6966941B1 (en) Sewage sludge treatment
JP2010168542A (en) System and apparatus for manufacturing fuel, bedding and fertilizer from livestock excrement
EP4046970A1 (en) Process for treating residual biological sludge for the production of granular fertilizer
US6214064B1 (en) Process for making a fuel product from coal fines and sewage sludge
PT840711E (en) PROCESS FOR TREATING RESIDUAL LAMPS
CN201704181U (en) Sludge alkalinity stabilizing and drying treatment device
JPS5950087A (en) Livestock excrements treatment and device
EP0480030B1 (en) Method and apparatus for composting mixture of livestock excretion and barn mat
JP2007333334A (en) Circulation-type organic matter drying/water separation treatment method
CN113666609B (en) Sludge dewatering treatment system and sludge treatment method
KR100945233B1 (en) Method of treating sludge for recycled soil, curing apparatus for the method and system for treating sludge for recycled soil using the apparatus
JPS5845798A (en) Treatment of organic or inorganic sludge
PL236690B1 (en) Method of producing raw meal, dried clay granules and baked clay granules and the production line of raw meal, dried clay granules and baked clay granules
JP2005138074A (en) Material obtained by stabilizing waste
CN100475729C (en) Sludge carrier drying process
JP2008115020A (en) Livestock feces fertilizing device
JPH11106773A (en) Preparation of solid fuel from muddy substance
CN215610861U (en) Stirring and heating equipment for water-soluble fertilizer production
RU2125548C1 (en) Method and installation for production of granulated organic-based fertilizers