JP2000072579A - Apparatus for treating excreta of livestock - Google Patents

Apparatus for treating excreta of livestock

Info

Publication number
JP2000072579A
JP2000072579A JP24609198A JP24609198A JP2000072579A JP 2000072579 A JP2000072579 A JP 2000072579A JP 24609198 A JP24609198 A JP 24609198A JP 24609198 A JP24609198 A JP 24609198A JP 2000072579 A JP2000072579 A JP 2000072579A
Authority
JP
Japan
Prior art keywords
tank
liquid
deodorizing
livestock
pipe
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.)
Withdrawn
Application number
JP24609198A
Other languages
Japanese (ja)
Inventor
Haruji Ajita
春次 味田
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.)
NISSO PLANT KENSETSU KK
SHINTO ECO TECHNO KK
ZEORA CHEMICAL KK
Original Assignee
NISSO PLANT KENSETSU KK
SHINTO ECO TECHNO KK
ZEORA CHEMICAL 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 NISSO PLANT KENSETSU KK, SHINTO ECO TECHNO KK, ZEORA CHEMICAL KK filed Critical NISSO PLANT KENSETSU KK
Priority to JP24609198A priority Critical patent/JP2000072579A/en
Publication of JP2000072579A publication Critical patent/JP2000072579A/en
Withdrawn legal-status Critical Current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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/20Sludge processing

Landscapes

  • Housing For Livestock And Birds (AREA)
  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
  • Treating Waste Gases (AREA)
  • Treatment Of Sludge (AREA)
  • Fertilizers (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide an apparatus for treating excreta of livestock without affecting the outside of facilities by treating the excreta of the livestock animals or a malodor generating from the excreta in the facilities. SOLUTION: This apparatus for treating excreta of livestock is equipped with a solid-liquid separating device 4 for obtaining liquid excreta 6 from discharged excreta 3 of the livestock animals, a cylindrical vertical type treating tank 11 having a hopper-shaped lower part, a secondary fermenter 15 for providing a liquid fertilizer 17, a hollow cylindrical type deodorizing and heat insulating tank 19 in which a deodorizing material layer 20 comprising an organic material having the heat insulating effects is formed in the interior, a first duct 22 for sucking and feeding a malodor 23 filled in a barn 1 to the hollow cylindrical type deodorizing and heat insulating tank 19 and a second duct 24 for discharging air in the hollow cylindrical type deodorizing and heat insulating tank 19 to the atmosphere. The liquid fertilizer 17 is sprinkled over the barn 1 and the deodorizing material layer 20, deodorized, sterilized and then sucked from the second duct 24 to thereby pass the malodor 23 taken into the hollow cylindrical type deodorizing and heat insulating tank 19 through the deodorizing material layer 20 and deodorize the malodor 23.

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、畜産動物の液体糞
尿を曝気した後に光合成細菌により発酵処理し、次い
で、曝気処理して得られた液肥を畜舎等の脱臭・殺菌に
利用する畜産動物の排泄物処理装置に関するものであ
る。
BACKGROUND OF THE INVENTION The present invention relates to a livestock animal which uses a liquid fertilizer obtained by aerating liquid manure of a livestock animal with a photosynthetic bacterium and then aerating the liquid manure for deodorization and sterilization in a livestock barn. The present invention relates to an excrement disposal device.

【0002】[0002]

【従来の技術】周知の通り、近年、遠隔地の市街化によ
り郊外の酪農施設に住宅が近接し、徐々に酪農家と地域
住民との混住化が進んでいる。
2. Description of the Related Art As is well known, in recent years, houses have become closer to suburban dairy facilities due to urbanization in remote areas, and dairy farmers and local residents have gradually been mixed.

【0003】[0003]

【発明が解決しようとする課題】しかし、酪農施設は畜
産動物の排泄物から発生する悪臭を放つため、地域住民
にとっては悪臭公害となり、酪農家にとっては酪農施設
の移転や離農等、畜産経営に深い影を落としている。そ
のため、地域社会の一員として畜産経営を継続するため
に環境保全についての配慮、努力が要求され、悪臭を放
さない酪農施設が切望されている。
However, dairy facilities emit bad odors from the excrement of livestock animals, causing odor pollution to local residents, and dairy farmers to relocate dairy facilities or leave farming for livestock management. It casts a deep shadow. Therefore, consideration and efforts for environmental preservation are required in order to continue livestock management as a member of the local community, and dairy facilities that do not emit bad odors are eagerly needed.

【0004】そこで、本発明は、畜産動物の排泄物や該
排泄物から発生する悪臭を施設内で処理して施設外には
影響を及ぼさない畜産動物の排泄物処理装置を提供する
ことを技術的課題として、その具現化をはかるべく研
究、実験を重ねた結果、畜産動物の液体糞尿を曝気して
光合成細菌により発酵処理する処理槽内では光合成細菌
や好気性微生物等が溶存酸素を利用して液体糞尿中の有
機物を栄養源として増殖するため、該有機物は高速に酸
化されると共に、液温は60℃以上まで上昇して急激な発
酵が促進され、その結果、当該液体糞尿は発酵処理され
た液となること、この発酵処理液を更に悪臭のない黒褐
色の粘性が低下した液体になるまで曝気処理すれば、ス
カムがほとんどない取り扱いやすい完熟した液肥になる
こと、そして、当該完熟液肥はこれらの物性の他に生物
活性を合わせ持っているため、畜舎の床洗浄用やスプレ
ー散布用に用いて畜舎内の脱臭、殺菌に利用できること
に着目し、当該完熟液肥を利用すれば、微生物活性に富
んだ脱臭が可能となり、安定した高悪臭除去効率の脱臭
処理が実現できるという刮目すべき知見を得、前記技術
的課題を達成したものである。
Therefore, the present invention provides a livestock animal excrement disposal apparatus that treats excrement of livestock animals and offensive odors generated from the excretions in a facility and does not affect outside the facility. As a technical challenge, as a result of repeated research and experiments to realize this, photosynthetic bacteria and aerobic microorganisms use dissolved oxygen in a treatment tank where liquid manure of livestock animals is aerated and fermented by photosynthetic bacteria. As the organic matter in the liquid manure grows as a nutrient source, the organic matter is rapidly oxidized, and the liquid temperature rises to 60 ° C. or higher to promote rapid fermentation. As a result, the liquid manure is subjected to the fermentation treatment. If this fermentation treatment liquid is further aerated until it becomes a black-brown, viscous liquid with no foul odor, it becomes an easy-to-handle ripe liquid fertilizer with almost no scum. Since the mature liquid fertilizer has biological properties in addition to these physical properties, it can be used for deodorizing and sterilizing the animal barn for washing the floor of the barn and spraying. In addition, the present inventors have obtained remarkable knowledge that deodorization rich in microbial activity can be achieved, and that a deodorizing treatment with a stable and high odor removal efficiency can be realized.

【0005】[0005]

【課題を解決するための手段】前記技術的課題は、次の
通りの本発明によって解決できる。
The technical problem can be solved by the present invention as described below.

【0006】即ち、本発明に係る畜産動物の排泄物処理
装置は、畜舎1から搬送されてきた畜産動物の排泄糞尿
3から固形物5を分離して液体糞尿6を得る固液分離装
置4と、当該固液分離装置4に第一移送管13を介して連
結されて該第一移送管13を通って送られてきた前記液体
糞尿6を曝気して光合成細菌により発酵処理して発酵処
理液12を得るホッパー状下部26を有する筒状竪型処理槽
11と、当該筒状竪型処理槽11に第二移送管16を介して連
結されて該第二移送管16を通って送られてきた前記発酵
処理液12をさらに曝気処理して液肥17を得る二次発酵槽
15と、当該二次発酵槽15から前記畜舎1まで配管されて
前記液肥17を畜舎1に送り出す第三移送管18と、前記筒
状竪型処理槽11の周囲を包囲して一体的に周設されて内
部に保温効果を有する有機資材からなる脱臭材層20が形
成されている中空筒型脱臭・保温槽19と、当該中空筒型
脱臭・保温槽19と前記二次発酵槽15とを連結して脱臭材
層20に液肥17を供給する第四移送管21と、前記中空筒型
脱臭・保温槽19から畜舎1まで配管されて畜舎1内に充
満した悪臭23を中空筒型脱臭・保温槽19に吸送する第一
ダクト22と、前記中空筒型脱臭・保温槽19に接続されて
中空筒型脱臭・保温槽19内の空気を吸引して大気に排出
する第二ダクト24とを備えており、前記液肥17を畜舎1
及び脱臭材層20に散布して脱臭・殺菌すると共に、前記
第二ダクト24より吸引することにより中空筒型脱臭・保
温槽19を経由して畜舎1内を減圧状態にして前記第一ダ
クト22を通って中空筒型脱臭・保温槽19に取り込まれた
悪臭23を脱臭材層20に通過させて脱臭するものである。
That is, the livestock excrement disposal apparatus according to the present invention comprises a solid-liquid separation device 4 for separating solids 5 from livestock excrement 3 conveyed from the livestock barn 1 to obtain liquid manure 6. The liquid manure 6 connected to the solid-liquid separation device 4 via the first transfer pipe 13 and sent through the first transfer pipe 13 is aerated, and fermented by photosynthetic bacteria to obtain a fermentation treatment liquid. A cylindrical vertical processing tank having a hopper-shaped lower part 26 for obtaining 12
11, the fermentation treatment liquid 12 connected to the cylindrical vertical treatment tank 11 via the second transfer pipe 16 and sent through the second transfer pipe 16 to further aerate the liquid fertilizer 17. Secondary fermentation tank to get
A third transfer pipe 18, which is piped from the secondary fermentation tank 15 to the livestock house 1 and sends out the liquid fertilizer 17 to the livestock house 1; A hollow cylindrical deodorizing and heat retaining tank 19 in which a deodorizing material layer 20 made of an organic material having a heat retaining effect is formed therein, and the hollow cylindrical deodorizing and heat retaining tank 19 and the secondary fermentation tank 15 are formed. A fourth transfer pipe 21 connected to supply the liquid fertilizer 17 to the deodorizing material layer 20; and a hollow cylindrical deodorizing / A first duct 22 that sucks and sucks the heat into the heat retaining tank 19, and a second duct 24 that is connected to the hollow cylindrical deodorizing and heat retaining tank 19 and sucks air in the hollow cylindrical deodorizing and heat retaining tank 19 and discharges the air to the atmosphere. And the liquid fertilizer 17
The deodorizing material layer 20 is sprayed and deodorized and sterilized, and the inside of the barn 1 is depressurized through the hollow cylindrical deodorizing and heat retaining tank 19 by suctioning from the second duct 24, and the first duct 22 is decompressed. The offensive odor 23 taken into the hollow cylindrical deodorizing / insulation tank 19 through the deodorizing material layer 20 is deodorized.

【0007】また、本発明は、前記畜産動物の排泄物処
理装置において、液肥17を、1m3の液体糞尿6に対して
光合成細菌を20〜30g 加えて50〜75時間曝気した発酵処
理液12をさらに50〜75時間曝気して悪臭のない黒褐色の
低粘性液体とした完熟液肥としたものである。
Further, according to the present invention, there is provided the excrement disposal device for livestock animals, wherein the liquid fertilizer 17 is added with 20 to 30 g of photosynthetic bacteria to 1 m 3 of liquid manure 6 and aerated for 50 to 75 hours. Was further aerated for 50 to 75 hours to obtain a ripe liquid fertilizer having a black-brown, low-viscosity liquid free of offensive odor.

【0008】さらに、本発明は、前記いずれかの畜産動
物の排泄物処理装置において、有機資材が、おが屑、籾
殻、麦殻、豆殻、落花生殻、細断した稲藁及び細断した
麦藁から少なくとも一つ選ばれるものである。
Further, according to the present invention, in any of the above livestock animal excrement disposal apparatuses, the organic material comprises sawdust, rice hull, wheat husk, bean husk, peanut hull, shredded rice straw and shredded wheat straw. At least one is chosen.

【0009】[0009]

【発明の実施の形態】以下、本発明の実施の形態を図面
に基づき説明する。
Embodiments of the present invention will be described below with reference to the drawings.

【0010】図1は本発明に係る畜産動物の排泄物処理
装置を説明するブロック図、図2は図1に示す畜舎、固
液分離装置及び分離液貯留槽を模型的に図示した説明
図、図3は図1に示す筒状竪型処理槽、中空筒型脱臭・
保温槽及び二次発酵槽を模型的に図示した一部断面側面
図、図4は図3に示す中空筒型脱臭・保温槽の平面図で
あり、中空筒型脱臭・保温槽への配管以外の配管は省略
している。また、図5は図3に示す筒状竪型処理槽の消
泡装置を図示した縦断面側面図、図6は図5に示す消泡
装置のA−A’線断面図である。
FIG. 1 is a block diagram for explaining a livestock animal excrement disposal apparatus according to the present invention. FIG. 2 is an explanatory view schematically showing a livestock house, a solid-liquid separation device, and a separated liquid storage tank shown in FIG. FIG. 3 shows a cylindrical vertical processing tank shown in FIG.
FIG. 4 is a plan view of the hollow cylindrical deodorizing / insulating tank shown in FIG. 3, except for piping to the hollow cylindrical deodorizing / insulating tank. Are omitted. FIG. 5 is a vertical sectional side view showing the defoaming device of the cylindrical vertical processing tank shown in FIG. 3, and FIG. 6 is a sectional view taken along line AA 'of the defoaming device shown in FIG.

【0011】これらの図において、1は酪農施設内に建
てられた畜舎、2は畜舎1内の排泄糞尿、該排泄糞尿が
付着した藁及びおが屑等の敷料(以下、これらを一括し
て「排泄糞尿」という。)3を集めて搬出するバンクリ
ーナ、4はバンクリーナ2で搬送されてきた排泄糞尿3
をホッパー4aで受けて該排泄糞尿3から固形物5を分離
して液体糞尿6を得る固液分離装置、7は固液分離装置
4から排出される固形物5を堆肥舎8まで移送するベル
トコンベア、9は固液分離装置4で分離される液体糞尿
6を取り出す送出管、10は送出管9を通って送られてき
た液体糞尿6を一時溜めておく分離液貯留槽、11は液体
糞尿6を曝気して光合成細菌により発酵処理して発酵処
理液12を得る筒状竪型処理槽(以下、単に「処理槽」と
いう。)、13は前記送出管9と分離液貯留槽10とを介し
て固液分離装置4と処理槽11とを連結する流入管(第一
移送管)であり、14は分離液貯留槽10内に設置された該
分離液貯留槽10の液体糞尿6を流入管13を通過させて処
理槽11に送くる移送ポンプ、15は処理槽11に流出管(第
二移送管)16を介して連結されて該流出管16を通って送
られてきた発酵処理液12をさらに曝気処理して悪臭のな
い粘性が低下した黒褐色の液体(以下、単に「完熟液
肥」という。)17を得る二次発酵槽、18は二次発酵槽15
から畜舎1内まで配管されて完熟液肥17を畜舎1に送り
出す供給管(第三移送管)、19は処理槽11の周囲を包囲
して一体的に周設されて内部に保温効果を有する有機資
材からなる脱臭材層20(図3参照)が形成されている中
空筒型脱臭・保温槽(以下、単に「脱臭槽」とい
う。)、21は脱臭槽19と二次発酵槽15とを連結して脱臭
槽19の脱臭材層20に完熟液肥17を供給する供給管(第四
移送管)、22は畜舎1から脱臭槽19まで配管されて畜舎
1内に充満した悪臭23を脱臭槽19に吸送する第一吸引ダ
クト(第一ダクト)、24は脱臭槽19と吸引ファン25とを
連結して脱臭槽19内の空気を吸引して大気に排出する第
二吸引ダクト(第二ダクト)である。
In these figures, reference numeral 1 denotes a livestock barn built in a dairy farm, 2 denotes litter excreted in the barn 1 and litter such as straw and sawdust to which the excreted urine adheres (hereinafter collectively referred to as “excretion”). The excrement 3 collected and carried out by the bank cleaner 4 and the excreted manure 3 carried by the
And a solid-liquid separator for separating the solid matter 5 from the excreted manure 3 to obtain liquid manure 6, and a belt 7 for transferring the solid matter 5 discharged from the solid-liquid separator 4 to the compost house 8. Conveyor, 9 is a delivery pipe for taking out liquid manure 6 separated by solid-liquid separation device 4, 10 is a separated liquid storage tank for temporarily storing liquid manure 6 sent through delivery pipe 9, and 11 is liquid manure. A cylindrical vertical processing tank (hereinafter simply referred to as “processing tank”) for aerating 6 and fermenting with photosynthetic bacteria to obtain a fermentation treatment liquid 12, and 13 is provided with the delivery pipe 9 and the separated liquid storage tank 10. An inflow pipe (first transfer pipe) for connecting the solid-liquid separation device 4 to the processing tank 11 through the intermediation of the liquid manure 6 in the separated liquid storage tank 10 installed in the separated liquid storage tank 10 A transfer pump for feeding the processing tank 11 through the pipe 13 is connected to the processing tank 11 through an outflow pipe (second transfer pipe) 16. The fermentation treatment liquid 12 sent through the outlet pipe 16 is further aerated to obtain a black-brown liquid 17 (hereinafter simply referred to as “ripe liquid fertilizer”) 17 having a low viscosity without odor. , 18 is the secondary fermenter 15
And a supply pipe (third transfer pipe) 19, which pipes the mature liquid fertilizer 17 to the stable 1 and surrounds the periphery of the treatment tank 11, and is an organic material having a heat retaining effect therein. A hollow cylindrical deodorizing / insulating tank (hereinafter, simply referred to as a “deodorizing tank”) having a deodorizing material layer 20 (see FIG. 3) made of materials, and 21 connects the deodorizing tank 19 and the secondary fermentation tank 15 A supply pipe (fourth transfer pipe) for supplying the mature liquid fertilizer 17 to the deodorizing material layer 20 of the deodorizing tank 19, and a pipe 22 is connected from the livestock barn 1 to the deodorizing tank 19 to remove the odor 23 filled in the livestock house 1 from the deodorizing tank 19. A first suction duct (first duct) for sucking air into the air, and a second suction duct (second duct) for connecting the deodorizing tank 19 and the suction fan 25 to suction air in the deodorizing tank 19 and discharging the air to the atmosphere ).

【0012】前記処理槽11の下部26はホッパー状に形成
されており、処理槽11内の下部26近傍には、噴射口27a
を中央部まで伸ばして位置付けされているL字形上向き
噴射器27と処理槽11の底26a 近傍まで伸ばして位置付け
されている液体糞尿吸込口28とを設けた曝気ポンプ29が
配設され、曝気ポンプ29には外気を取り入れる吸気管30
が接続され、吸気管30の吸気口30a は処理槽11の上部31
から突出して設けられている。そして、曝気ポンプ29の
噴射器27には他端を処理槽11の近傍に設置された曝気ブ
ロア32に接続した曝気用エア管33が連結されている。
The lower portion 26 of the processing tank 11 is formed in a hopper shape.
And an aeration pump 29 provided with an L-shaped upward injector 27 extending to the center and a liquid manure suction port 28 extending to near the bottom 26a of the processing tank 11. 29 has an intake pipe 30 that takes in outside air
Is connected, and the suction port 30a of the suction pipe 30 is connected to the upper portion 31 of the processing tank 11.
It is provided so as to protrude from. An aeration air pipe 33 having the other end connected to an aeration blower 32 installed near the processing tank 11 is connected to the injector 27 of the aeration pump 29.

【0013】処理槽11内の中央部には、噴射器27の噴射
口27a を下端部34a にて外包している煙突状エアーリフ
ト管34が鉛直に立設され、エアーリフト管34の上端部34
b は処理槽11に満たされる液体糞尿6の液面から突き出
す位置に位置付けられており、該上端部34b には隙間を
有して泡を発生させる陣笠状覆い35が取り付けられてい
る。また、処理槽11の上部31中央は開口しており、該開
口部31a には泡を上方へ導く円筒状センターウエル(泡
ガイド筒管)36が当該開口部31a からエアーリフト管34
を囲んで液面下方位置まで延出して設けられている。ま
た、センターウエル36の上端開口部36a は截頭円錐状に
形成されており、当該開口部36a には、プロペラ37の打
撃により泡を叩き潰してスラリー状処理物38にする消泡
装置39が連結されている。
A chimney-shaped air-lift tube 34 surrounding the injection port 27a of the injector 27 at a lower end portion 34a is provided vertically at a central portion in the processing tank 11, and an upper end portion of the air-lift tube 34 is provided. 34
The b is positioned at a position protruding from the liquid surface of the liquid manure 6 filled in the processing tank 11, and a cap-like cover 35 for generating bubbles with a gap is attached to the upper end 34b. The center of the upper portion 31 of the processing tank 11 is open, and a cylindrical center well (bubble guide tube) 36 for guiding bubbles upward is provided in the opening 31a.
And extends to a position below the liquid level. Further, the upper end opening 36a of the center well 36 is formed in a truncated conical shape, and a defoaming device 39 that smashes bubbles by a blow of a propeller 37 to form a slurry-like processed material 38 is provided in the opening 36a. Are linked.

【0014】処理槽11の上部31には、光合成細菌体を処
理槽11に投入するための投入口40が設けられていると共
に、液体糞尿6を処理槽11に送り込む前記流入管13が処
理槽11内に貫通させて連結されている。
In the upper part 31 of the treatment tank 11, an inlet 40 for introducing photosynthetic bacteria into the treatment tank 11 is provided, and the inflow pipe 13 for feeding the liquid manure 6 into the treatment tank 11 is connected to the treatment tank 11. It is connected by penetrating into 11.

【0015】処理槽11の下部26近傍には、他端を液体糞
尿6を一次溜めておく分離液貯留槽10に接続したオーバ
ーフロー管41と処理槽11で生成された発酵処理液12であ
る上澄み液を取り出す前記流出管16とがそれぞれ当該処
理槽11を貫通して連結され、処理槽11内で上方に伸び、
オーバーフロー管41においては先端のフロー口41a を前
記エアーリフト管34の上端部34b に届かない高さに位置
付けられ、流出管16においては先端の流出口16a を前記
フロー口41a が位置付けられた高さに対して2/3の高
さに位置付けられている。さらに、処理槽11の底26a に
は、処理槽11に溜まった砂や砂利等の沈殿物を取り出す
取出口42が設けられている。
In the vicinity of the lower portion 26 of the processing tank 11, the other end is an overflow pipe 41 connected to the separated liquid storage tank 10 for temporarily storing the liquid manure 6 and the supernatant which is the fermentation processing liquid 12 generated in the processing tank 11. The outflow pipes 16 for taking out the liquid are connected to each other through the processing tank 11, and extend upward in the processing tank 11,
In the overflow pipe 41, the front flow port 41a is positioned at a height that does not reach the upper end 34b of the air lift pipe 34, and in the outflow pipe 16, the front outlet port 16a is positioned at a height at which the flow port 41a is positioned. Is positioned at a height of 2/3. Further, an outlet 42 for taking out sediment such as sand and gravel accumulated in the processing tank 11 is provided at the bottom 26a of the processing tank 11.

【0016】消泡装置39は、図5及び図6に示すよう
に、プロペラ37を備えた消泡機43とセンターウエル36の
上端開口部36a 側に設けられた円形内壁44及び消泡機43
側に設けられた円形外壁45により形成されてプロペラ37
を囲んでいるリング状回廊46とからなり、前記円形内壁
44はプロペラ37を外周しており、前記円形外壁45は円形
内壁44を遠巻きに外周している。そして、リング状回廊
46の一方側にはリング状回廊46内に溜まるスラリー状処
理物38を洗い流す洗浄液流入口47が設けられ、他方側に
は排出溝48が形成されている。そして、消泡装置39は排
出溝48側に向かって傾斜させてセンターウエル36の上端
開口部36a に取り付けられている。
As shown in FIGS. 5 and 6, the defoaming device 39 includes a defoaming device 43 having a propeller 37, a circular inner wall 44 provided on the upper end opening 36a side of the center well 36, and a defoaming device 43.
The propeller 37 is formed by a circular outer wall 45 provided on the side.
And a ring-shaped corridor 46 surrounding the circular inner wall.
Reference numeral 44 denotes the outer periphery of the propeller 37, and the circular outer wall 45 extends around the circular inner wall 44 in a far winding manner. And the ring corridor
A cleaning liquid inflow port 47 is provided on one side of the ring-shaped corridor 46 to wash out the slurry-like processed material 38 accumulated in the ring-shaped corridor 46, and a discharge groove 48 is formed on the other side. The defoaming device 39 is attached to the upper end opening 36a of the center well 36 while being inclined toward the discharge groove 48 side.

【0017】なお、49は排出溝48の排出口、50は排出口
49に連結された、スラリー状処理物38を送り出す排水シ
ュート管(図3参照)、51はセンターウエル36内を洗浄
するための洗浄口である。
Reference numeral 49 denotes a discharge port of the discharge groove 48, and 50 denotes a discharge port.
A drain chute pipe (see FIG. 3) connected to 49 for sending out the slurry-like processed material 38, and 51 is a cleaning port for cleaning the inside of the center well 36.

【0018】脱臭槽19において、脱臭槽19の内部には、
おが屑、籾殻、麦殻、豆殻、落花生殻、細断した稲藁及
び細断した麦藁から少なくとも一つ選ばれる有機資材か
らなる保温効果を有する脱臭材層20と砂利等からなる台
層52が形成されており、脱臭槽19の形状は円筒形中空筒
型の横断面リング状に形成されており、脱臭槽19の上面
には、脱臭槽19内に前記有機資材を投入する投入口53と
完熟液肥17を脱臭材層20に供給する供給口54(図4参
照)とが設けられており、該供給口54には一端を二次発
酵槽15内に設置された供給ポンプ55に接続した前記供給
管21が接続されている。そして、供給口54は脱臭槽19内
の上部を一周するリング管56(図4参照)に繋がってお
り、リング管56の下面には等間隔にスプレー口57(図4
参照)が開口している。また、脱臭槽19の上端部には、
脱臭槽19内の空気を吸引して排出する排出口58(図4参
照)が設けられ、該排出口58には他端を処理槽11の近傍
に設置された吸引ファン25に接続した前記第二吸引ダク
ト24が接続されている。
In the deodorizing tank 19, inside the deodorizing tank 19,
Sawdust, rice husk, wheat husk, pea husk, peanut hull, deodorizing material layer 20 having a heat retaining effect composed of at least one organic material selected from shredded rice straw and shredded wheat straw, and a bed layer 52 composed of gravel, etc. It is formed, the shape of the deodorizing tank 19 is formed in the shape of a cross section of a cylindrical hollow cylinder type, on the upper surface of the deodorizing tank 19, an input port 53 for charging the organic material into the deodorizing tank 19 and A supply port 54 (see FIG. 4) for supplying the fully-ripened liquid fertilizer 17 to the deodorizing material layer 20 is provided, and one end of the supply port 54 is connected to a supply pump 55 provided in the secondary fermentation tank 15. The supply pipe 21 is connected. The supply port 54 is connected to a ring pipe 56 (see FIG. 4) that goes around the upper part in the deodorization tank 19, and the spray port 57 (FIG.
Open). Also, at the upper end of the deodorization tank 19,
An outlet 58 (see FIG. 4) for sucking and discharging the air in the deodorizing tank 19 is provided, and the other end of the outlet 58 is connected to the suction fan 25 installed near the processing tank 11. Two suction ducts 24 are connected.

【0019】脱臭槽19の下端部には、畜舎1で発生した
悪臭23を取り込む取込口59が設けられていると共に、脱
臭槽19内の有機資材を取り出す取出口60が前記下端部を
一周して設けられおり、取込口59には畜舎1に配管され
た前記第一吸引ダクト22が接続されている。また、脱臭
槽19の下面には、脱臭槽19の底に溜まった完熟液肥17を
二次発酵槽15へ戻す排出管61が接続されている。
At the lower end of the deodorizing tank 19, an intake port 59 for taking in the odor 23 generated in the barn 1 is provided, and an outlet port 60 for taking out the organic material in the deodorizing tank 19 extends around the lower end section. The first suction duct 22 connected to the stable 1 is connected to the intake port 59. A discharge pipe 61 for returning the mature liquid fertilizer 17 collected at the bottom of the deodorization tank 19 to the secondary fermentation tank 15 is connected to the lower surface of the deodorization tank 19.

【0020】二次発酵槽15において、前記排水シュート
管50、流出管16及び排出管61の出口が臨む位置には流れ
込んだ発酵処理液12及びスラリー状処理物38を網目を通
して二次発酵槽15内に流すスクリーン槽62が設けられ、
二次発酵槽15内には、他端を二次発酵槽15の外に設置さ
れた曝気ブロア63に接続したエア管64と二次発酵槽15で
生成される完熟液肥17を取り出す流出管65とが配設され
ており、エア管64の先端近傍には上向きに気泡が噴出す
る噴射ノズル66が取り付けられている。なお、67は一端
を二次発酵槽15に接続されたダクトであり、他端は第一
吸引ダクト22に連結されている。また、流出管65は完熟
液肥17を貯蔵する既設地下ピット(図示せず。)に接続
されており、既設地下ピット内の完熟液肥17は必要に応
じて畜舎以外の悪臭を放つ酪農施設に脱臭のために散布
され、また、圃場に施肥のために散布される。また、二
次発酵槽15内には前記供給ポンプ55が設置されており、
該供給ポンプ55には前記供給管21が接続され、供給管21
には前記供給管18が連結されている。
In the secondary fermentation tank 15, the fermentation treatment liquid 12 and the slurry-like processed material 38 flowing into the secondary fermentation tank 15 are passed through the mesh at positions where the outlets of the drain chute 50, the outflow pipe 16 and the discharge pipe 61 face. A screen tank 62 flowing in is provided,
In the secondary fermentation tank 15, an air pipe 64 having the other end connected to an aeration blower 63 installed outside the secondary fermentation tank 15, and an outflow pipe 65 for extracting the mature liquid fertilizer 17 generated in the secondary fermentation tank 15 In the vicinity of the tip of the air pipe 64, an ejection nozzle 66 for ejecting bubbles upward is attached. In addition, 67 is a duct having one end connected to the secondary fermentation tank 15, and the other end is connected to the first suction duct 22. In addition, the outflow pipe 65 is connected to an existing underground pit (not shown) for storing the mature liquid fertilizer 17, and the mature liquid fertilizer 17 in the existing underground pit is deodorized to a stinking dairy facility other than the livestock barn as necessary. And fertilized on the field. Further, the supply pump 55 is installed in the secondary fermentation tank 15,
The supply pipe 55 is connected to the supply pipe 21,
Is connected to the supply pipe 18.

【0021】次に、排泄糞尿3と悪臭23の流れについて
説明する。
Next, the flow of the excrement 3 and the odor 23 will be described.

【0022】畜舎1内の畜産動物から排泄された排泄糞
尿3はバンクリーナ2で集められて固液分離装置4に搬
送されて固液分離装置4のホッパー4aに入る。固液分離
装置4では排泄糞尿3が固形物5と液体糞尿6に分離さ
れて固形物5はベルトコンベア7で堆肥舎8に移送され
る。
Excrement 3 excreted from livestock animals in the barn 1 is collected by the bank cleaner 2, conveyed to the solid-liquid separator 4, and enters the hopper 4 a of the solid-liquid separator 4. In the solid-liquid separation device 4, the excreted manure 3 is separated into solid matter 5 and liquid manure 6, and the solid matter 5 is transferred to a composting room 8 by a belt conveyor 7.

【0023】液体糞尿6は送出管9を通って分離液貯留
槽10に溜まる。分離液貯留槽10内の液体糞尿6は移送ポ
ンプ14で送り出され、流入管13を通って処理槽11に注ぎ
込まれる。オーバーフロー管41のフロー口41a を越えて
液体糞尿6が注ぎ込まれると、溢れた液体糞尿6はフロ
ー口41a からオーバーフロー管41を通って分離液貯留槽
10に送り込まれる。このとき流出管16は閉じられてい
る。液体糞尿6がフロー口41a まで満たされた後、流入
管13は閉じられ、投入口40から凍結光合成細菌体が投入
される。
The liquid manure 6 passes through the delivery pipe 9 and accumulates in the separated liquid storage tank 10. The liquid manure 6 in the separated liquid storage tank 10 is sent out by the transfer pump 14 and poured into the processing tank 11 through the inflow pipe 13. When the liquid manure 6 is poured over the flow port 41a of the overflow pipe 41, the overflowing liquid manure 6 passes through the overflow pipe 41 from the flow port 41a and the separated liquid storage tank.
Sent to 10. At this time, the outflow pipe 16 is closed. After the liquid manure 6 is filled up to the flow port 41a, the inflow tube 13 is closed, and the frozen photosynthetic bacterial body is introduced from the introduction port 40.

【0024】続いて、曝気ポンプ29が駆動され、処理槽
11内の液体糞尿6が吸込口28から吸い上げられ、夏場に
おいては吸気口30a から取り入れられた外気と混合され
て噴射器27からエアーリフト管34内に噴射される。ま
た、冬場においては吸気口30aは閉じられ、処理槽11の
近傍に設置された曝気ブロア32から圧縮熱風がエア管33
を通って噴射器27に送られ、液体糞尿6は熱風と混ざり
合って温められた状態でエアーリフト管34内に噴射され
る。曝気ポンプ29の曝気により空気と共に攪拌された液
体糞尿6は好気発酵されながら気泡混合状態でエアーリ
フト管34内を上昇し、エアーリフト管34の上端部34b か
ら吹き上げられて泡発生用の陣笠状覆い35に衝突してさ
らに発泡する。
Subsequently, the aeration pump 29 is driven and the processing tank
The liquid manure 6 in 11 is sucked up from the suction port 28, mixed with the outside air taken in from the suction port 30 a in summer, and injected into the air lift pipe 34 from the injector 27. In winter, the intake port 30a is closed, and compressed hot air is supplied from the aeration blower 32 installed near the processing tank 11 to the air pipe 33.
The liquid manure 6 is injected into the air lift pipe 34 while being heated while being mixed with the hot air. The liquid manure 6 stirred together with air by the aeration of the aeration pump 29 rises in the air lift pipe 34 in a bubble-mixed state while being aerobically fermented, and is blown up from the upper end 34b of the air lift pipe 34 to form bubbles for generating bubbles. The foam collides with the cover 35 and foams further.

【0025】覆い35に衝突して発生した泡は消泡機43の
プロペラ37の回転により吸引され、截頭円錐状に形成さ
れて狭くなった上端開口部36a で加速されて消泡装置39
の回廊46に送り込まれる際に、プロペラ37により叩き潰
され、さらに、外壁45と内壁44とに衝突して叩きつけら
れてスラリー状処理物38となり回廊46に溜まる。回廊46
に溜まったスラリー状処理物38は流入口47より送り込ま
れた洗浄液(例えば、完熟液肥17)と共に傾斜した回廊
46を通って排出溝48へ流れ出して排水シュート管50へ流
れ落ちる。
The foam generated by colliding with the cover 35 is sucked by the rotation of the propeller 37 of the defoamer 43, accelerated by the narrow upper end opening 36a formed in a truncated cone, and defoamed by the defoaming device 39.
When it is sent into the corridor 46, it is crushed by the propeller 37, collides with the outer wall 45 and the inner wall 44, and is slammed into a slurry-like processed material 38, which accumulates in the corridor 46. Corridor 46
The slurry-like processed material 38 accumulated in the sloping corridor along with the washing liquid (for example, ripe liquid fertilizer 17) sent from the inflow port 47
It flows out through 46 into a drain 48 and down into a drain chute 50.

【0026】一方、好気発酵されながら気泡混合状態で
エアーリフト管34内を上昇した大半の液体糞尿6はセン
ターウエル36内を下降し、吸込口28へ吸い込まれる液体
糞尿6の流れによってできた液流に乗って処理槽11の下
部26へ下降し、再び、吸込口28から吸い上げられてエア
ーリフト管34内に噴射される。
On the other hand, most of the liquid manure 6 which has risen in the air-lift tube 34 in a bubble-mixed state while undergoing aerobic fermentation is formed by the flow of the liquid manure 6 which descends in the center well 36 and is sucked into the suction port 28. It rides on the liquid flow, descends to the lower part 26 of the processing tank 11, is sucked up again from the suction port 28, and is injected into the air lift pipe 34.

【0027】所望時間(例えば、75時間/9m3液体糞尿
量)繰り返された後、流出管16が開けられ、フロー口41
a の水位から流出口16a までの水位にある上澄み液であ
る発酵処理液12が流出管16を通って二次発酵槽15のスク
リーン槽62に入り、発酵処理液12に含まれている脱毛等
の不溶解物が濾過されて二次発酵槽15に流れ落ちる。こ
のとき二次発酵槽15の流出管65は閉じられている。
After repetition for a desired time (for example, 75 hours / 9 m 3 of liquid manure), the outlet pipe 16 is opened and the flow port 41 is opened.
The fermentation treatment liquid 12, which is the supernatant liquid at the water level from the water level a to the outlet 16a, enters the screen tank 62 of the secondary fermentation tank 15 through the outflow pipe 16, and removes the hair contained in the fermentation treatment liquid 12, etc. Are filtered and flow down to the secondary fermenter 15. At this time, the outflow pipe 65 of the secondary fermentation tank 15 is closed.

【0028】流出口16a の位置の水位となった処理槽11
では、流入管13が開けられてフロー口41a の位置まで液
体糞尿6が補充されて発酵処理が繰り返される。
The treatment tank 11 at the water level at the outlet 16a
Then, the inflow pipe 13 is opened, the liquid manure 6 is replenished to the position of the flow port 41a, and the fermentation process is repeated.

【0029】二次発酵槽15に溜まったスラリー状処理物
38と発酵処理液12とは、曝気ブロア63からエア管64を通
って噴射ノズル66から噴射される圧縮熱風によって曝気
攪拌されることにより、さらに、好気発酵される。
Slurry-like processed material accumulated in the secondary fermentation tank 15
The aerobic fermentation is further performed on the 38 and the fermentation treatment liquid 12 by aeration and agitation by compressed hot air injected from the injection nozzle 66 through the air pipe 64 from the aeration blower 63.

【0030】二次発酵槽15において、所望時間(例え
ば、75時間/9m3発酵処理液量)曝気処理して悪臭のな
い粘性の低下した黒褐色の液体となれば、完熟液肥17と
して供給ポンプ55によって供給管21を通って脱臭槽19の
供給口54に送られる。また、一部の完熟液肥17は流出管
18を通って畜舎1内、バンクリーナ2及び各糞尿処理施
設周辺に散布され、臭気発生の抑制やウィルス病の予防
等に利用される。また、前記スラリー状処理物38の洗浄
液としても利用される。
In the secondary fermentation tank 15, if a black-brown liquid with no odor and reduced viscosity is obtained by aeration treatment for a desired time (for example, 75 hours / 9 m 3 of fermentation treatment liquid), the supply pump 55 is supplied as the mature liquid fertilizer 17. Is supplied to the supply port 54 of the deodorization tank 19 through the supply pipe 21. In addition, some ripe liquid fertilizers 17
It is sprayed through the pen 18 to the inside of the barn 1, the bank cleaner 2 and the vicinity of each manure processing facility, and is used for suppressing odor generation and preventing virus diseases. It is also used as a cleaning liquid for the slurry-like processed material 38.

【0031】供給ポンプ55によって脱臭槽19の供給口54
に送られた完熟液肥17は、リング管56のスプレー口57か
ら脱臭材層20へ散布される。
The supply port 55 of the deodorization tank 19 is supplied by the supply pump 55.
Is fed to the deodorizing material layer 20 from the spray port 57 of the ring tube 56.

【0032】完熟液肥17を所要量(例えば、有機資材37
0gに対して900 リットル)散布した後、吸引ファン25を
駆動して吸引すれば、脱臭槽19内や畜舎1内が減圧状態
となり、畜舎1に配管された第一吸引ダクト22から悪臭
23が脱臭槽19内へ圧送される。脱臭槽19内へ圧送された
悪臭23は脱臭材層20を通過する過程で悪臭物質を好んで
利用する光合成細菌を含む有機資材と接触して生物学的
脱臭が行われ、無臭状態となって脱臭槽19の排出口58か
ら第二吸引ダクト24へ排出されて大気へ放散される。
The required amount of the mature liquid fertilizer 17 (for example, organic material 37)
After spraying (900 liters per 0 g), if the suction fan 25 is driven and sucked, the inside of the deodorization tank 19 and the livestock house 1 will be in a decompressed state, and the first suction duct 22 piped to the livestock house 1 will cause odor.
23 is pumped into the deodorizing tank 19. The odor 23 pumped into the deodorization tank 19 comes into contact with an organic material containing photosynthetic bacteria, which prefers and uses odorous substances, in the process of passing through the deodorization material layer 20, and is subjected to biological deodorization to become odorless. The air is discharged from the outlet 58 of the deodorization tank 19 to the second suction duct 24 and is released to the atmosphere.

【0033】初回の完熟液肥17の散布の後、の間欠散布
(例えば、1時間毎に15リットル)を実施すると共に、
脱臭する。
After the first application of the mature liquid fertilizer 17, intermittent application (for example, 15 liters per hour) is performed.
Deodorizes.

【0034】本発明においては、処理槽11をホッパー状
下部26を有する円筒形竪型に形成し、処理槽11内の中央
部に、曝気エアーを上昇させるエアーリフト管34と該エ
アーリフト管34を囲んで液面下まで延びたセンターウエ
ル36とを設けたので、センターウエル36内に泡を発生さ
せることができるから、泡が処理槽11の液面全体に広が
ることがなく、効率よく消泡することができ、液体糞尿
6を吸引する吸込口28をホッパー状下部26に位置付けて
処理槽11の中央部では上向きに液流を起こしていると共
に、吸込口28へ吸い込まれる液体糞尿6により下向きの
液流を起こしているから、処理槽11内の液体糞尿6が淀
むことなくホッパー状下部26に集まり、均一な発酵処理
を行うことができ、そして、処理槽11で得られた発酵処
理液12を二次発酵槽15でさらに曝気処理して脱臭・殺菌
用として利用できる完熟液肥17(悪臭のない粘性の低下
したスカムのほとんどない取り扱いやすい黒褐色の液
体)を得ているので、施設内で生じた畜産動物の排泄糞
尿3や該排泄糞尿3から発生する悪臭23を施設内で処理
することができる。
In the present invention, the processing tank 11 is formed in a cylindrical vertical shape having a hopper-like lower portion 26, and an air lift pipe 34 for raising aeration air and an air lift pipe 34 And a center well 36 extending below the liquid level is provided, so that bubbles can be generated in the center well 36, so that the bubbles do not spread over the entire liquid level of the processing tank 11 and are efficiently erased. A suction port 28 that can foam and sucks the liquid manure 6 is positioned in the hopper-shaped lower part 26, and a liquid flow is generated upward in the center of the processing tank 11, and the liquid manure 6 is sucked into the suction port 28. Due to the downward liquid flow, the liquid manure 6 in the treatment tank 11 collects in the hopper-like lower part 26 without stagnation, and can perform a uniform fermentation treatment, and the fermentation treatment obtained in the treatment tank 11 Liquid 12 is further added to secondary fermenter 15 A matured liquid fertilizer 17 (black-brown liquid with no bad smell and low viscosity and almost no scum with low viscosity) that can be used for deodorization and sterilization by aeration treatment is used. The malodor 23 generated from the excrement 3 can be treated in the facility.

【0035】また、付帯効果として、消泡装置39におい
ては、発生した泡はプロペラ37により叩き潰されると共
に、回廊46の内壁44と外壁45に衝突することでも潰され
るので、泡の残らないスラリー処理物38となり、さら
に、消泡装置39は排出溝48側に向かって傾斜させてセン
ターウエル36の上端開口部36a に設けられているので、
スラリー状処理物38が泡により回廊46に付着することな
く洗浄液で洗い流されて排出される。
Further, as an incidental effect, in the defoaming device 39, the generated foam is crushed by the propeller 37 and also crushed by colliding with the inner wall 44 and the outer wall 45 of the corridor 46. It becomes a processed material 38, and furthermore, since the defoaming device 39 is provided at the upper end opening 36a of the center well 36 by being inclined toward the discharge groove 48 side,
The slurry-like processed material 38 is washed away with the cleaning liquid without being attached to the corridor 46 by the foam, and is discharged.

【0036】また、処理槽11においては、液体糞尿6内
の不溶性固形物はホッパー状下部26に集中して溜まるの
で、取出口42から容易に取り出すことができる。
Further, in the treatment tank 11, the insoluble solids in the liquid manure 6 are collected and concentrated in the hopper-shaped lower part 26, so that they can be easily taken out from the outlet 42.

【0037】また、脱臭槽19においては、液体糞尿6を
曝気して光合成細菌により発酵処理する筒状竪型の処理
槽11の周囲を包囲するように中空筒型の脱臭槽19を一体
的に設けたので、別途脱臭槽を設置する敷地面積を必要
とせず、建設費によるコスト高が解消される。
In the deodorizing tank 19, a hollow cylindrical deodorizing tank 19 is integrally formed so as to surround the cylindrical vertical processing tank 11 for aerating the liquid manure 6 and performing fermentation treatment with photosynthetic bacteria. Since it is provided, there is no need for a site area for separately installing a deodorizing tank, and high costs due to construction costs are eliminated.

【0038】また、脱臭槽19内には、おが屑、籾殻、麦
殻、豆殻、落花生殻、細断した稲藁又は細断した麦藁等
の保温効果を有する有機資材からなる脱臭材層20を形成
すると共に、脱臭材層20に処理槽11で得た発酵処理液12
を更に曝気処理してなる完熟液肥17を散布するようにし
たので、60℃以上になる処理槽11内の発酵処理液12は、
冬期においても脱臭槽19の脱臭材層20により保温状態と
なり、処理槽11内の温度低下が抑えられて10〜40℃が適
温とされる生物活性に影響を与えることがない。また、
脱臭材層20の温度は冬期においては処理槽11内の温度に
より保持されるので、脱臭効果が損なわれることはな
い。さらに、長時間脱臭に使用された有機資材は、スカ
ムのほとんどない取り扱いやすい完熟液肥17を含んでい
るので、好気発酵後、堆肥肥料として圃場利用できるた
め、産業廃棄物とはならないという利点がある。
In the deodorizing tank 19, a deodorizing material layer 20 made of an organic material having a heat-retaining effect such as sawdust, rice husk, wheat husk, pea husk, peanut hull, shredded rice straw or shredded wheat straw is provided. The fermentation treatment liquid 12 obtained in the treatment tank 11
The fermented solution 12 in the treatment tank 11 at 60 ° C. or higher was sprayed with the mature liquid fertilizer 17 which was further aerated.
Even in winter, the deodorizing material layer 20 of the deodorizing tank 19 keeps the temperature, and the temperature in the processing tank 11 is suppressed from being lowered, so that the biological activity of 10 to 40 ° C. is not affected. Also,
Since the temperature of the deodorizing material layer 20 is maintained in winter by the temperature in the processing tank 11, the deodorizing effect is not impaired. Furthermore, the organic material used for long-time deodorization contains an easy-to-handle ripe liquid fertilizer 17 with almost no scum, so that it can be used in the field as a compost fertilizer after aerobic fermentation, so that it does not become an industrial waste. is there.

【0039】なお、処理槽11及び脱臭槽19は横断面多角
形の筒型であってもよい。また、悪臭の圧送効率を上げ
るために、砂利等からなる台層52を設けたが、当該台層
52を省略してもよい。また、処理槽11及び脱臭槽19はス
テンレス製とすればよい。また、第一吸引ダクト22は畜
舎1に配管されているが、堆肥舎8等の他の糞尿処理施
設にも配管されていてもよい。
The processing tank 11 and the deodorizing tank 19 may have a cylindrical shape with a polygonal cross section. In order to increase the efficiency of pumping odors, a bed layer 52 made of gravel was provided.
52 may be omitted. Further, the processing tank 11 and the deodorizing tank 19 may be made of stainless steel. Further, the first suction duct 22 is connected to the livestock barn 1, but may be connected to another manure processing facility such as the compost bar 8.

【0040】有機資材は、おが屑、籾殻、麦殻、豆殻、
落花生殻、細断した稲藁及び細断した麦藁等を単独或い
は複数混合したものを用いればよい。
Organic materials include sawdust, rice husk, wheat husk, bean husk,
Peanut hulls, shredded rice straw, shredded wheat straw and the like may be used alone or in combination.

【0041】また、光合成細菌は市販の凍結菌体を用い
ればよく、光合成細菌の投入量は液体糞尿1m3に対して
5〜50g であればよく、環境条件にもよるが5g未満で
は不活性又は不安定となりやすく、50g を越える量を投
入しても増量に比例した効果は得られず、経費上好まし
くない。もっとも好ましいのは20〜30g である。
As the photosynthetic bacterium, commercially available frozen cells may be used. The input amount of the photosynthetic bacterium may be 5 to 50 g per 1 m 3 of liquid manure, and depending on environmental conditions, it is inactive at less than 5 g. Or, it tends to be unstable, and if the amount exceeds 50 g, the effect proportional to the increase is not obtained, which is not preferable in terms of cost. Most preferred is 20-30 g.

【0042】平均外気温度30℃の夏期においては、2日
間(50時間)〜3時間(75時間)の50時間に近い時間曝
気して発酵処理した発酵処理液12を更に2日間(50時
間)〜3時間(75時間)の50時間に近い時間曝気処理す
れば、また、平均外気温度−10℃の冬期においては、2
日間(50時間)〜3時間(75時間)の75時間に近い時間
曝気して発酵処理した発酵処理液12を更に2日間(50時
間)〜3時間(75時間)の75時間に近い時間曝気処理す
れば、悪臭のない粘性が低下した黒褐色の液体のスカム
がほとんどない取り扱いやすい完熟液肥17となる。当該
完熟液肥17は生物の棲息に必要な水分、栄養分及び活性
に富んだ微生物をバランスよく含んだ脱臭液である。
In the summertime at an average outside air temperature of 30 ° C., the fermented solution 12 which has been aerated for 2 days (50 hours) to 3 hours (75 hours) for about 50 hours and fermented is further added for 2 days (50 hours). If the aeration process is performed for about 3 hours (75 hours), which is close to 50 hours, and in winter when the average outside temperature is −10 ° C.,
Fermentation solution 12 fermented by aeration for about 75 hours for 3 days (75 hours) for 3 days (75 hours) for 2 days (50 hours) to 3 hours (75 hours) for about 75 hours If it is treated, it becomes an easy-to-handle ripe liquid fertilizer 17 that has almost no odor and has almost no scum of a black-brown liquid with reduced viscosity. The fully matured liquid fertilizer 17 is a deodorant liquid containing a well-balanced amount of water, nutrients, and active microorganisms necessary for living organisms.

【0043】完熟液肥17の脱臭材層20への散布量は、初
回は有機資材370kg に対して800 〜1,000 リットルと
し、この後の補充散布は、稼働中、10〜20リットル/1
時間であればよく、夏期では最小値に近い散布量とし、
冬期では最大値に近い散布量とすればよい。
The amount of the mature liquid fertilizer 17 applied to the deodorizing material layer 20 is initially 800 to 1,000 liters with respect to 370 kg of the organic material.
It is sufficient if it is time, and in summer, the spraying amount is close to the minimum value,
In winter, the spraying amount may be close to the maximum value.

【0044】吸引ファン25による吸引は1,100 〜1,300m
3 /時とすれば、効率よく脱臭できる。
The suction by the suction fan 25 is 1,100 to 1,300 m
If it is 3 / hour, it can be efficiently deodorized.

【0045】リング管56は脱臭槽19の上面上方に設けら
れていてもよい。この場合、供給管21はリング管56に連
結され、完熟液肥17の供給口54は脱臭槽19の上面に等間
隔に複数設けられてリング管56と連結され、スプレー口
57は脱臭槽19内において供給口54と接続すればよい。
The ring tube 56 may be provided above the upper surface of the deodorization tank 19. In this case, the supply pipe 21 is connected to a ring pipe 56, and the supply ports 54 of the mature liquid fertilizer 17 are provided at equal intervals on the upper surface of the deodorization tank 19 and connected to the ring pipe 56, and the spray port is provided.
57 may be connected to the supply port 54 in the deodorization tank 19.

【0046】[0046]

【実施例】北海道野付郡別海町において実施した。経産
牛100 頭の排泄物5トン/日を固液分離機4(スクリュ
ープレス:動力3.7kw )に通して固形物5を分離し、液
体糞尿6を得た。該液体糞尿6を下部26がホッパー状の
ステンレス製円筒形竪型処理槽11(内容量:9m3,円筒
部の直径:2m ,円筒部の高さ:約3.15m )に9m3注ぎ
込んで、投入口40より凍結光合成細菌体(1012生菌体/
g)を225g投入した。
[Example] Conducted in Betsukai-cho, Notsuke-gun, Hokkaido. The excrement of 5 tons / day of 100 multiparous cows was passed through a solid-liquid separator 4 (screw press: power 3.7 kw) to separate the solid 5 to obtain liquid manure 6. Liquid manure 6 the lower 26 of the hopper-shaped stainless steel cylindrical vertical treatment vessel 11 (internal volume: 9m 3, the cylindrical portion of diameter: 2m, the cylindrical portion height: about 3.15M) in 9m 3 poured in, Freezing photosynthetic bacteria (10 12 viable cells /
g) was charged in an amount of 225 g.

【0047】また、ステンレス製中空円筒形脱臭・保温
槽19(内容量:2.3m3 ,外円の直径:2.45m ,高さ:3.
15m )の内部に砂利からなる深さ25cmの台層52とおが屑
からなる深さ2.5mの脱臭材層20を形成した。
Also, a stainless steel hollow cylindrical deodorizing / insulating tank 19 (content: 2.3 m 3 , outer circle diameter: 2.45 m, height: 3.
15 m), a bed layer 52 of 25 cm in depth made of gravel and a deodorizing material layer 20 of 2.5 m in depth made of sawdust were formed.

【0048】外気温度27℃の夏期に、曝気ポンプ29(エ
ゼクター付循環水中ポンプ:空気量供給能力:20m3/時
×1.5kw )と泡消機43(気密型300rpm×0.2kw )とを駆
動した。約70時間程度循環曝気したところ、液体糞尿6
は64℃に昇温した。この時点で発酵処理を終了し、フロ
ー口41a の水位から流出口16a までの水位にある3m3
発酵処理液12を二次発酵槽15(内容量:9m3)に入れ、
処理槽11には液体糞尿6を3m3補充して凍結光合成細菌
体を75g 投入すると共に、二次発酵槽15では、曝気ブロ
ア63(0.1kg/m2×0.35m3/分×0.4kw ×25A )を駆動
し、再度、約70時間程度曝気した。二次発酵槽15内の発
酵処理液12は悪臭のない粘性が低下した黒褐色の液体
(完熟液肥)17となった。このときの完熟液肥17の温度
は41℃であった。
In the summer time when the outside air temperature is 27 ° C., the aeration pump 29 (circulating submersible pump with ejector: air supply capacity: 20 m 3 /hour×1.5 kw) and the bubble erasing machine 43 (airtight type 300 rpm × 0.2 kw) are driven. did. After about 70 hours of circulation aeration, liquid manure 6
Rose to 64 ° C. At this point, the fermentation treatment is terminated, and 3 m 3 of the fermentation treatment liquid 12 at the water level from the flow port 41 a to the outlet 16 a is put into the secondary fermentation tank 15 (content: 9 m 3 ).
The treatment tank 11 is replenished with 3 m 3 of liquid manure 6 and charged with 75 g of frozen photosynthetic bacteria, and the secondary fermentation tank 15 has an aeration blower 63 (0.1 kg / m 2 × 0.35 m 3 /min×0.4 kw × 25A) was driven and again aerated for about 70 hours. The fermentation treatment liquid 12 in the secondary fermentation tank 15 became a black-brown liquid (ripe liquid fertilizer) 17 having a low viscosity without a bad smell. The temperature of the mature liquid fertilizer 17 at this time was 41 ° C.

【0049】続いて、供給ポンプ55(0.05m3/分×7m
×0.25kw×40A )を駆動して50リットル/分の完熟液肥
17を脱臭・保温槽19内の脱臭材層20に20分散布した。こ
のときの脱臭・保温槽19内の温度は43℃であった。
Subsequently, the supply pump 55 (0.05 m 3 / min × 7 m
× 0.25kw × 40A) to drive 50 liters / min of mature liquid fertilizer
17 was dispersed and dispersed in a deodorizing material layer 20 in a deodorizing / heating tank 19. At this time, the temperature in the deodorization / insulation tank 19 was 43 ° C.

【0050】この後、吸引ファン25(750m3/時×150mmA
q ×1.5kw )を駆動して畜舎1及び糞尿処理施設に配管
された第一吸引ダクト22から悪臭23を脱臭・保温槽19内
に吸引した。このとき、畜舎1内は2〜3mmAqの減圧状
態となった。悪臭吸引中、1時間毎に15リットルの完熟
液肥17を間欠散布した。
Thereafter, the suction fan 25 (750 m 3 / hour × 150 mmA
q × 1.5 kw) to drive the odor 23 from the first suction duct 22 piped to the livestock barn 1 and the manure processing facility into the deodorization / insulation tank 19. At this time, the inside of the barn 1 was in a reduced pressure state of 2-3 mmAq. During the odor suction, 15 liters of mature liquid fertilizer 17 was intermittently sprayed every hour.

【0051】悪臭23にはアンモニアが0.8ppm、トリメチ
ルアミンが0.004ppm含まれていたが、第二吸引ダクト24
から出てきた気体中にはいずれも含まれていなかった。
The odor 23 contained 0.8 ppm of ammonia and 0.004 ppm of trimethylamine.
Out of the gas did not contain any.

【0052】外気温度−10℃の冬期において実施したと
ころ、液体糞尿6は59℃に昇温し、完熟液肥17の温度は
35℃であった。また、脱臭・保温槽19内の温度は37℃で
あった。
When the test was carried out in winter at an outside air temperature of −10 ° C., the temperature of the liquid manure 6 was raised to 59 ° C.
35 ° C. The temperature in the deodorizing / insulating tank 19 was 37 ° C.

【0053】悪臭23にはアンモニアが7.6ppm、トリメチ
ルアミンが0.035ppm含まれていたが、第二吸引ダクト24
から出てきた気体中にはいずれも含まれていなかった。
The odor 23 contained 7.6 ppm of ammonia and 0.035 ppm of trimethylamine.
Out of the gas did not contain any.

【0054】[0054]

【発明の効果】以上説明した通り、本発明によれば、畜
産動物の排泄物から悪臭を消臭する液肥を生成して該液
肥を利用して施設内で発生する悪臭を消臭すると共に、
排泄物の残り滓は液肥を散布することにより肥料として
利用できるから、施設外に影響を及ぼさない畜産動物の
排泄物処理装置を提供することができる。
As described above, according to the present invention, a liquid manure for deodorizing malodor is produced from the excrement of livestock animals, and the liquid fertilizer is used to deodorize the malodor generated in the facility.
Since the residue of excrement can be used as fertilizer by spraying liquid fertilizer, it is possible to provide an excrement disposal device for livestock animals that does not affect the outside of the facility.

【0055】従って、本発明の産業上利用性は非常に高
いといえる。
Therefore, it can be said that the industrial applicability of the present invention is very high.

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

【図1】本発明に係る畜産動物の排泄物処理装置を説明
するブロック図である。
FIG. 1 is a block diagram illustrating a livestock animal excrement disposal apparatus according to the present invention.

【図2】図1に示す畜舎、固液分離装置及び分離液貯留
槽を模型的に図示した説明図である。
FIG. 2 is an explanatory diagram schematically showing the livestock house, the solid-liquid separation device, and the separated liquid storage tank shown in FIG.

【図3】図1に示す筒状竪型処理槽、中空筒型脱臭・保
温槽及び二次発酵槽を模型的に図示した一部断面側面図
である。
FIG. 3 is a partial cross-sectional side view schematically showing a cylindrical vertical processing tank, a hollow cylindrical deodorizing and heat retaining tank, and a secondary fermentation tank shown in FIG.

【図4】図3に示す中空筒型脱臭・保温槽の平面図であ
る。
FIG. 4 is a plan view of the hollow cylindrical deodorizing and heat retaining tank shown in FIG.

【図5】図3に示す筒状竪型処理槽の消泡装置を図示し
た縦断面側面図である。
FIG. 5 is a vertical cross-sectional side view illustrating a defoaming device of the cylindrical vertical processing tank shown in FIG.

【図6】図5に示す消泡装置のA−A’線断面図であ
る。
6 is a sectional view taken along line AA ′ of the defoaming device shown in FIG.

【符号の説明】[Explanation of symbols]

1 畜舎 3 排泄糞尿 4 固液分離装置 5 固形物 6 液体糞尿 9 送出管 10 分離液貯留槽 11 処理槽 12 発酵処理液 13 流入管 15 二次発酵槽 16 流出管 17 完熟液肥 18 供給管 19 脱臭槽 21 供給管 22 第一吸引ダクト 23 悪臭 24 第二吸引ダクト DESCRIPTION OF SYMBOLS 1 Cattle barn 3 Excreted manure 4 Solid-liquid separation device 5 Solid matter 6 Liquid manure 9 Delivery pipe 10 Separation liquid storage tank 11 Processing tank 12 Fermentation treatment liquid 13 Inflow pipe 15 Secondary fermentation tank 16 Outflow pipe 17 Ripe liquid fertilizer 18 Supply pipe 19 Deodorization Vessel 21 Supply pipe 22 First suction duct 23 Odor 24 Second suction duct

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) // A61L 9/01 (72)発明者 味田 春次 福島県岩瀬郡岩瀬村大字畑田字みどりが丘 2番地 Fターム(参考) 2B101 CB01 4C080 AA07 BB02 BB04 BB05 BB06 CC13 HH05 MM31 MM33 MM40 NN24 QQ11 QQ17 QQ20 4D002 AA13 AA14 AA40 AB02 AC10 BA17 CA01 CA07 CA20 DA59 DA66 EA06 EA07 GA01 GB06 HA01 4D059 AA02 BA02 BA25 BE01 BE51 BK01 CA08 CA10 CA17 CA22 CC01 DB32 DB33 EA16 EB11 4H061 AA03 CC37 DD20 EE61 EE64 EE66 FF01 GG48 GG70 HH42 HH44 JJ01 LL05 LL26 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) // A61L 9/01 (72) Inventor Haruji Haruka, Iwase-mura, Iwase-gun, Fukushima Prefecture F-term (reference) 2B101 CB01 4C080 AA07 BB02 BB04 BB05 BB06 CC13 HH05 MM31 MM33 MM40 NN24 QQ11 QQ17 QQ20 4D002 AA13 AA14 AA40 AB02 AC10 BA17 CA01 CA07 CA20 DA59 DA66 EA06 EA07 GA01 BA01 CA01 BA01 CA02 CC01 DB32 DB33 EA16 EB11 4H061 AA03 CC37 DD20 EE61 EE64 EE66 FF01 GG48 GG70 HH42 HH44 JJ01 LL05 LL26

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 畜舎1から搬送されてきた畜産動物の排
泄糞尿3から固形物5を分離して液体糞尿6を得る固液
分離装置4と、当該固液分離装置4に第一移送管13を介
して連結されて該第一移送管13を通って送られてきた前
記液体糞尿6を曝気して光合成細菌により発酵処理して
発酵処理液12を得るホッパー状下部26を有する筒状竪型
処理槽11と、当該筒状竪型処理槽11に第二移送管16を介
して連結されて該第二移送管16を通って送られてきた前
記発酵処理液12をさらに曝気処理して液肥17を得る二次
発酵槽15と、当該二次発酵槽15から前記畜舎1まで配管
されて前記液肥17を畜舎1に送り出す第三移送管18と、
前記筒状竪型処理槽11の周囲を包囲して一体的に周設さ
れて内部に保温効果を有する有機資材からなる脱臭材層
20が形成されている中空筒型脱臭・保温槽19と、当該中
空筒型脱臭・保温槽19と前記二次発酵槽15とを連結して
脱臭材層20に液肥17を供給する第四移送管21と、前記中
空筒型脱臭・保温槽19から畜舎1まで配管されて畜舎1
内に充満している悪臭23を中空筒型脱臭・保温槽19に吸
送する第一ダクト22と、前記中空筒型脱臭・保温槽19に
接続されて中空筒型脱臭・保温槽19内の空気を吸引して
大気に排出する第二ダクト24とを備えており、前記液肥
17を畜舎1及び脱臭材層20に散布して脱臭・殺菌すると
共に、前記第二ダクト24より吸引することにより中空筒
型脱臭・保温槽19を経由して畜舎1内を減圧状態にして
前記第一ダクト22を通って中空筒型脱臭・保温槽19に取
り込まれた悪臭23を脱臭材層20に通過させて脱臭するこ
とを特徴とする畜産動物の排泄物処理装置。
1. A solid-liquid separator 4 for separating solids 5 from excrement 3 of livestock animals transported from the barn 1 to obtain liquid manure 6, and a first transfer pipe 13 connected to the solid-liquid separator 4. A cylindrical vertical type having a hopper-shaped lower part 26 for aerating the liquid manure 6 which has been sent through the first transfer pipe 13 and being fermented by photosynthetic bacteria to obtain a fermentation treatment liquid 12. The fermentation treatment liquid 12 which is connected to the treatment tank 11 and the cylindrical vertical treatment tank 11 via the second transfer pipe 16 and sent through the second transfer pipe 16 is further subjected to aeration treatment to obtain a liquid fertilizer. A second fermentation tank 15 that obtains 17, a third transfer pipe 18 that is piped from the secondary fermentation tank 15 to the livestock house 1 and sends out the liquid fertilizer 17 to the livestock house 1;
A deodorizing material layer made of an organic material which is integrally provided around the periphery of the cylindrical vertical processing tank 11 and has a heat retaining effect therein.
The fourth transfer for supplying the liquid fertilizer 17 to the deodorizing material layer 20 by connecting the hollow cylindrical deodorizing and heat retaining tank 19 and the secondary fermentation tank 15 to the hollow cylindrical deodorizing and heat retaining tank 19 in which 20 is formed. A pipe 21 and a pipe extending from the hollow cylindrical deodorizing / insulating tank 19 to the stable 1
The first duct 22 that sucks the odor 23 filled therein into the hollow cylinder type deodorization / insulation tank 19 and the inside of the hollow cylinder type deodorization / insulation tank 19 connected to the hollow cylinder type deodorization / insulation tank 19. A second duct 24 for sucking air and discharging the air to the atmosphere,
17 is sprayed on the livestock house 1 and the deodorizing material layer 20 to deodorize and sterilize, and the inside of the livestock house 1 is depressurized through the hollow cylindrical deodorizing and heat retaining tank 19 by sucking from the second duct 24, and An excrement disposal device for livestock animals, characterized in that the malodor 23 taken into the hollow cylindrical deodorizing / insulating tank 19 through the first duct 22 is passed through the deodorizing material layer 20 for deodorization.
【請求項2】 液肥17が、1m3の液体糞尿6に対して光
合成細菌を20〜30g加えて50〜75時間曝気した発酵処理
液12をさらに50〜75時間曝気して悪臭のない黒褐色の低
粘性液体とした完熟液肥である請求項1記載の畜産動物
の排泄物処理装置。
2. A liquid fertilizer 17 is prepared by adding 20 to 30 g of photosynthetic bacteria to 1 m 3 of liquid manure 6 and aerating the fermentation solution 12 for 50 to 75 hours for another 50 to 75 hours. 2. The livestock excrement disposal apparatus according to claim 1, wherein the apparatus is a fully liquid fertilizer made of a low viscosity liquid.
【請求項3】 有機資材が、おが屑、籾殻、麦殻、豆
殻、落花生殻、細断した稲藁及び細断した麦藁から少な
くとも一つ選ばれるものである請求項1又は2記載の畜
産動物の排泄物処理装置。
3. The livestock animal according to claim 1, wherein the organic material is at least one selected from sawdust, rice husk, husk, bean husk, peanut hull, shredded rice straw, and shredded wheat straw. Excrement disposal equipment.
JP24609198A 1998-08-31 1998-08-31 Apparatus for treating excreta of livestock Withdrawn JP2000072579A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP24609198A JP2000072579A (en) 1998-08-31 1998-08-31 Apparatus for treating excreta of livestock

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP24609198A JP2000072579A (en) 1998-08-31 1998-08-31 Apparatus for treating excreta of livestock

Publications (1)

Publication Number Publication Date
JP2000072579A true JP2000072579A (en) 2000-03-07

Family

ID=17143367

Family Applications (1)

Application Number Title Priority Date Filing Date
JP24609198A Withdrawn JP2000072579A (en) 1998-08-31 1998-08-31 Apparatus for treating excreta of livestock

Country Status (1)

Country Link
JP (1) JP2000072579A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003053393A (en) * 2001-08-10 2003-02-25 Aoi Kosan:Kk Excreta treatment equipment
JP2005334778A (en) * 2004-05-27 2005-12-08 Miike Iron Works Co Ltd Method and equipment for fermenting organic waste
WO2015125795A1 (en) * 2014-02-19 2015-08-27 三井造船株式会社 Methane fermentation method and methane fermentation system
CN107999165A (en) * 2017-10-27 2018-05-08 无锡艾科瑞思产品设计与研究有限公司 A kind of wheat wipes skin detoxicating machine
CN109399767A (en) * 2018-08-20 2019-03-01 四川建元天地环保科技有限公司 A kind of poultry farming environment deodoration system and organic electrolyte are in purposes wherein
JP2021075445A (en) * 2019-11-08 2021-05-20 華南理工大学 Organic fertilizer production facility by chemical engineering energy cogeneration using feces of livestock and domestic fowl
WO2022267249A1 (en) * 2021-06-24 2022-12-29 海南宝秀节水科技股份有限公司 Method for adapting water and fertilizer integrated livestock excrement to growth of farmland plants

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003053393A (en) * 2001-08-10 2003-02-25 Aoi Kosan:Kk Excreta treatment equipment
JP2005334778A (en) * 2004-05-27 2005-12-08 Miike Iron Works Co Ltd Method and equipment for fermenting organic waste
JP4515825B2 (en) * 2004-05-27 2010-08-04 株式会社御池鐵工所 Fermentation treatment method for organic waste and its treatment equipment
WO2015125795A1 (en) * 2014-02-19 2015-08-27 三井造船株式会社 Methane fermentation method and methane fermentation system
CN107999165A (en) * 2017-10-27 2018-05-08 无锡艾科瑞思产品设计与研究有限公司 A kind of wheat wipes skin detoxicating machine
CN109399767A (en) * 2018-08-20 2019-03-01 四川建元天地环保科技有限公司 A kind of poultry farming environment deodoration system and organic electrolyte are in purposes wherein
JP2021075445A (en) * 2019-11-08 2021-05-20 華南理工大学 Organic fertilizer production facility by chemical engineering energy cogeneration using feces of livestock and domestic fowl
WO2022267249A1 (en) * 2021-06-24 2022-12-29 海南宝秀节水科技股份有限公司 Method for adapting water and fertilizer integrated livestock excrement to growth of farmland plants
JP2023534084A (en) * 2021-06-24 2023-08-08 海南宝秀▲節▼水科技股▲ふん▼有限公司 A method of adapting livestock manure combined with water and fertilizer to the growth of agricultural land plants
JP7402899B2 (en) 2021-06-24 2023-12-21 海南宝秀▲節▼水科技股▲ふん▼有限公司 A method for adapting livestock waste combined with water fertilizer to the growth of farmland plants

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