JP2003225696A - Apparatus for treating excreta of domestic animal and method for treating excreta of domestic animal by using the apparatus - Google Patents
Apparatus for treating excreta of domestic animal and method for treating excreta of domestic animal by using the apparatusInfo
- Publication number
- JP2003225696A JP2003225696A JP2002029187A JP2002029187A JP2003225696A JP 2003225696 A JP2003225696 A JP 2003225696A JP 2002029187 A JP2002029187 A JP 2002029187A JP 2002029187 A JP2002029187 A JP 2002029187A JP 2003225696 A JP2003225696 A JP 2003225696A
- Authority
- JP
- Japan
- Prior art keywords
- liquid
- tank
- decomposing
- decomposition
- livestock manure
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/20—Sludge processing
Landscapes
- Biological Treatment Of Waste Water (AREA)
- Treatment Of Sludge (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、牛、蓋、鶏等の家
畜の糞尿を微生物の作用で分解処理する家畜糞尿処理装
置及びこの処理装置による家畜糞尿処理方法に関するも
のである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a livestock excrement treating apparatus for decomposing feces of livestock such as cows, lids and chickens by the action of microorganisms, and a livestock excrement treating method using the treatment apparatus.
【0002】[0002]
【従来の技術】家畜糞尿を微生物の作用で分解処理する
ことは古くから行われている。この種の処理は、糞と尿
を分離し(固液分離)、固形分は固形分で、液状分は液
状分でそれぞれ別個に分解するのが通常である。この場
合において、どちらの成分も、微生物に利用され易い形
に前処理し、これを微生物の作用で分解している。尚、
これら糞尿を嫌気性菌によって分解すると、腐敗を起こ
して悪臭等を発生するから、好気性菌で分解するのが適
する。2. Description of the Related Art Decomposition of livestock excrement by the action of microorganisms has been performed for a long time. In this type of treatment, it is usual that feces and urine are separated (solid-liquid separation), and solid is decomposed into solid and liquid is decomposed into liquid separately. In this case, both components are pretreated so that they are easily utilized by microorganisms and decomposed by the action of microorganisms. still,
When these excrements are decomposed by anaerobic bacteria, they decompose and generate a bad odor, etc. Therefore, decomposition by aerobic bacteria is suitable.
【0003】[0003]
【発明が解決しようとする課題】従って、従来のこの種
の処理装置においては、どのような効果的な前処理を施
すか或いは如何にして好気的環境を維持するかが成否の
鍵となっていた。本発明は、このような課題を解決する
ものであり、固液分離した液状分を微生物の作用で分解
処理するにつき、好気性微生物の生育環境を高めてその
分解力を高めたものである。Therefore, in the conventional processing apparatus of this kind, what effective pretreatment or how to maintain the aerobic environment is the key to success or failure. Was there. The present invention is intended to solve such a problem and to enhance the growth environment of aerobic microorganisms and enhance their decomposing power when the solid-liquid separated liquid component is decomposed by the action of microorganisms.
【0004】[0004]
【課題を解決するための手段】この課題の下、本発明
は、請求項1に記載した、家畜糞尿を固液分離してそれ
ぞれ微生物の作用で分解処理する家畜糞尿処理装置にお
いて、液状分を分解処理する分解槽を複数設け、分解槽
の上流側にミネラル分が含まれる生命活性液が加えられ
る第一曝気槽を設けるとともに、下流側に表面を磨いた
カキ殻を浸漬した仕上槽を設けたことを特徴とする家畜
糞尿処理装置を提供したものである。Under the above problems, the present invention provides a livestock excrement treating apparatus for solid-liquid separating livestock excrement according to claim 1 and decomposing the same by the action of microorganisms. A plurality of decomposition tanks for decomposing treatment are provided, a first aeration tank to which the bioactive liquid containing minerals is added is provided on the upstream side of the decomposition tank, and a finishing tank in which a polished oyster shell is immersed is provided on the downstream side. The present invention provides an apparatus for treating livestock manure characterized by the above.
【0005】又、本発明は、請求項4に記載した、家畜
糞尿を固液分離してそれぞれ微生物の作用で分解処理す
る家畜糞尿処理装置による家畜糞尿処理方法であって、
液状分を分解処理する分解槽を複数設け、分解槽の上流
側の第一曝気槽にミネラル分が含まれる生命活性化液を
加えて微生物作用を活発化させ、下流側の仕上槽に表面
を磨いたカキ殻を浸漬して微生物の生育床としたことを
特徴とする家畜糞尿処理装置よる家畜糞尿処理方法を提
供する。The present invention also provides a livestock excrement treating method using a livestock excrement treating apparatus for solid-liquid separating livestock excrement and decomposing it by the action of microorganisms.
A plurality of decomposition tanks for decomposing liquid components are provided, and a bioactive liquid containing minerals is added to the first aeration tank on the upstream side of the decomposition tank to activate microbial action, and the surface is added to the finishing tank on the downstream side. Provided is a method for treating livestock excrement by a livestock excrement treating apparatus, which comprises immersing a polished oyster shell in a microbial growth bed.
【0006】液状分の曝気過程において、ミネラル分を
含む生命活性液を加えると、そのミネラル分が嫌気性菌
の活動を抑えて液状分を腐り難くするとともに、好気性
菌の栄養分となって繁殖を促す。更に、このミネラル分
は、空気中の波動エネルギーを吸収して液状分を活性化
するとも言われている。更に、分解槽の下流側を構成す
る仕上槽に表面を磨いたカキ殻を浸漬すると、カキ殻に
形成された微小孔が微生物の絶好の生育床となり、その
繁殖を促して分解を促進する。When a biologically active liquid containing minerals is added in the aeration process of the liquid content, the mineral content suppresses the activity of anaerobic bacteria and makes the liquid content less prone to decay, and also propagates as nutrients for aerobic bacteria. Encourage. Further, it is said that this mineral component absorbs wave energy in the air to activate the liquid component. Furthermore, when the oyster shell with a polished surface is immersed in a finishing tank constituting the downstream side of the decomposition tank, the micropores formed in the oyster shell serve as a perfect growth bed for microorganisms, promoting their growth and promoting decomposition.
【0007】以下、本発明の実施の形態を図面を参照し
て説明する。図1は本発明の一例を示す分解処理装置の
配置及びフロー図であるが、畜舎から出た糞尿はひとま
ず地下タンク1等に水を加えて貯留しておく。これをポ
ンプ2で汲み上げて固液分離器3に送り、ここで固形分
4と液状分5とに分ける。このうちの固形分4は堆肥に
するのであるが、それには、コンベア6等で堆肥舎7に
送り、適宜ショベル8等で切返しを行って発酵させる。
発酵して堆肥9となったものは、トラック10等で希望
農家に搬送したり、ストックヤード11で保管する。Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a layout and flow diagram of a decomposition treatment apparatus showing an example of the present invention. Manure discharged from a livestock barn is temporarily stored by adding water to an underground tank 1 or the like. This is pumped up by the pump 2 and sent to the solid-liquid separator 3, where it is separated into a solid content 4 and a liquid content 5. Of these, the solid content 4 is made into compost, which is sent to the compost house 7 by the conveyor 6 or the like and appropriately turned by the shovel 8 or the like to ferment it.
The fermented compost 9 is transported to a desired farm by a truck 10 or the like, or stored in the stockyard 11.
【0008】一方、液状分5については、一旦貯留槽1
2に集め、ここに水中ミキサー13で適宜攪拌しながら
溜めておく。これをポンプ14で分解槽15に送り、こ
こで分解するのであるが、本例における分解槽15は、
上流側から第一曝気槽16、第二曝気槽17、沈澱槽1
8、仕上槽19で構成されている。第一及び第二曝気槽
16、17による分解は、この中にブロワ20で空気を
送りながら液状分5を空気と接触させ、好気性菌の作用
で分解を行うものである。On the other hand, the liquid content 5 is once stored in the storage tank 1.
2 and collect them in the underwater mixer 13 with appropriate stirring. This is sent to the decomposition tank 15 by the pump 14 and decomposed here. The decomposition tank 15 in this example is
From the upstream side, the first aeration tank 16, the second aeration tank 17, the precipitation tank 1
8 and finishing tank 19. Decomposition by the first and second aeration tanks 16 and 17 is carried out by sending air through the blower 20 to bring the liquid component 5 into contact with air and performing decomposition by the action of aerobic bacteria.
【0009】本発明の特徴の一つは、最初の分解槽15
である第一曝気槽16にミネラル分を含む生命活性液2
1を加えることである。このミネラル分の添加により、
嫌気性菌の活動を抑えて液状分5を腐り難くするととも
に、これが好気性菌の栄養分となって繁殖を促す。更
に、このミネラル分は、空気中の波動エネルギーを吸収
して液状分5を活性化するとも言われている。One of the features of the present invention is that the first decomposition tank 15 is used.
The bioactive liquid 2 containing minerals in the first aeration tank 16
Is to add 1. By adding this mineral content,
The activity of the anaerobic bacteria is suppressed to make the liquid content 5 less likely to rot, and this serves as a nutrient for the aerobic bacteria to promote reproduction. Furthermore, it is said that this mineral component absorbs wave energy in the air to activate the liquid component 5.
【0010】第一曝気槽16で分解された液状分5は、
第二曝気槽17に移され、ここでも分解を継続されつ
つ、沈澱槽18に移される。尚、これらの移送は、溢流
や流下による自然移送でもよいし、ポンプ等で加圧する
強制移送でもよい。沈澱槽18に移された液状分5は、
その汚泥成分が底に溜まるから、これをポンプ22で第
一曝気槽16に還元し、分解を繰り返す。The liquid component 5 decomposed in the first aeration tank 16 is
It is moved to the second aeration tank 17 and is moved to the precipitation tank 18 while continuing to be decomposed here. The transfer may be natural transfer by overflow or downflow, or forced transfer by pressurizing with a pump or the like. The liquid content 5 transferred to the settling tank 18 is
Since the sludge component collects at the bottom, it is returned to the first aeration tank 16 by the pump 22, and the decomposition is repeated.
【0011】沈澱槽18内の液状分5は、仕上槽19に
移され、ここで仕上げ処理される。この仕上げ処理も、
ブロワ20で仕上槽19内に空気を送り(23はフィル
ター)、好気性菌による好気分解であるが、本発明で
は、この仕上槽19にカキ殻24を浸漬してこれで分解
を促進させるのである。The liquid component 5 in the settling tank 18 is transferred to a finishing tank 19 where it is finished. This finishing process also
The blower 20 sends air into the finishing tank 19 (23 is a filter) for aerobic decomposition by aerobic bacteria. In the present invention, the oyster shell 24 is immersed in the finishing tank 19 to accelerate the decomposition. Of.
【0012】図2はカキ殻24の斜視図であるが、ここ
で使用するカキ殻24は、その表面(表面及び裏面)を
磨いて表面に付いている海藻や泥を完全に落とすことが
肝要である。カキ殻24の表面には微小な孔が数多く形
成されており、これが微生物の生育床となるのである
が、海藻や泥が付いたままでは、孔が塞がってこの生育
床効果が十分に発揮されないからである。FIG. 2 is a perspective view of the oyster shell 24. It is essential that the surface (front and back) of the oyster shell 24 used here is polished to completely remove seaweed and mud attached to the surface. Is. Many micropores are formed on the surface of the oyster shell 24, and this serves as a growth bed for microorganisms. However, if seaweed or mud remains, the pores will be blocked and the growth bed effect will not be sufficiently exerted. Because.
【0013】図3はカキ殻24の浸漬状態を示す説明図
であるが、以上のカキ殻24を適当な網袋25に収納
し、これを仕上槽19内に吊るしておけばよい。このと
きに用いるカキ殻24の量は適宜でよいが、多い方が生
育床が増えて微生物の活動が活発になる。尚、カキ殻2
4は、炭酸カルシウムを主体としており、微生物の活動
によって溶解し、その量を減ずるから、減じた分だけ適
当に補充すればよい。FIG. 3 is an explanatory view showing how the oyster shells 24 are immersed, but the above oyster shells 24 may be housed in a suitable net bag 25 and hung in the finishing tank 19. The amount of the oyster shells 24 used at this time may be arbitrary, but the larger the number, the more the growth bed and the more active the microorganisms. In addition, oyster shell 2
4 is mainly composed of calcium carbonate, which is dissolved by the activity of microorganisms and its amount is reduced, so that it is sufficient to supplement the reduced amount appropriately.
【0014】このような分解を継続して行くと、液状分
5は、最終的には無害化された炭酸ガスと水とに分解さ
れるから、その水分をポンプ26で汲み上げ、農地等に
還元すればよい。又、最初の地下タンク1に戻し、添加
する水の増量剤又は代わりとしてもよい。When such decomposition is continued, the liquid content 5 is finally decomposed into detoxified carbon dioxide gas and water. Therefore, the water content is pumped up by the pump 26 and returned to farmland or the like. do it. Further, it may be returned to the first underground tank 1 and used as a filler or substitute for water to be added.
【0015】[0015]
【発明の効果】以上、本発明によれば、家畜糞尿の液状
分を処理するに際して生命活性水の添加やカキ殻の使用
によって好気分解が短時間でより完全に行われる。従っ
て、設備を大掛かりにする必要はなく、低コストで省ス
ペースのものできる。As described above, according to the present invention, the aerobic decomposition is completed more completely in a short time by adding the bioactive water and using the oyster shell when treating the liquid content of livestock excrement. Therefore, it is not necessary to make the equipment large, and the cost can be reduced and the space can be saved.
【図1】本発明の一例を示す家畜糞尿処理装置の配置及
びフロー図である。FIG. 1 is a layout and flow diagram of a livestock manure processing apparatus showing an example of the present invention.
【図2】本発明の一例を示すカキ殻の斜視図である。FIG. 2 is a perspective view of an oyster shell showing an example of the present invention.
【図3】本発明の一例を示すカキ殻を網袋に詰めた状態
の説明図である。FIG. 3 is an explanatory diagram showing a state in which an oyster shell according to an example of the present invention is packed in a net bag.
15 分解槽 16 第一曝気槽 19 仕上槽 21 生命活性液 24 カキ殻 25 網袋 15 Decomposition tank 16 First aeration tank 19 finishing tank 21 bioactive liquid 24 oyster shells 25 mesh bag
─────────────────────────────────────────────────────
─────────────────────────────────────────────────── ───
【手続補正書】[Procedure amendment]
【提出日】平成14年2月8日(2002.2.8)[Submission date] February 8, 2002 (2002.2.8)
【手続補正1】[Procedure Amendment 1]
【補正対象書類名】明細書[Document name to be amended] Statement
【補正対象項目名】全文[Correction target item name] Full text
【補正方法】変更[Correction method] Change
【補正内容】[Correction content]
【書類名】 明細書[Document name] Statement
【発明の名称】 家畜糞尿処理装置及びこの処理装置に
よる家畜糞尿処理方法Title: Livestock excrement treatment apparatus and livestock excrement treatment method using the treatment apparatus
【特許請求の範囲】[Claims]
【発明の詳細な説明】Detailed Description of the Invention
【0001】[0001]
【発明の属する技術分野】本発明は、牛、豚、鶏等の家
畜の糞尿を微生物の作用で分解処理する家畜糞尿処理装
置及びこの処理装置による家畜糞尿処理方法に関するも
のである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a livestock excrement treating apparatus for decomposing and treating the excrement of livestock such as cattle, pigs and chickens by the action of microorganisms, and a livestock excrement treating method using the treatment apparatus.
【0002】[0002]
【従来の技術】家畜糞尿を微生物の作用で分解処理する
ことは古くから行われている。この種の処理は、糞と尿
を分離し(固液分離)、固形分は固形分で、液状分は液
状分でそれぞれ別個に分解するのが通常である。この場
合において、どちらの成分も、微生物に利用され易い形
に前処理し、これを微生物の作用で分解している。尚、
これら糞尿を嫌気性菌によって分解すると、腐敗を起こ
して悪臭等を発生するから、好気性菌で分解するのが適
する。2. Description of the Related Art Decomposition of livestock excrement by the action of microorganisms has been performed for a long time. In this type of treatment, it is usual that feces and urine are separated (solid-liquid separation), and solid is decomposed into solid and liquid is decomposed into liquid separately. In this case, both components are pretreated so that they are easily utilized by microorganisms and decomposed by the action of microorganisms. still,
When these excrements are decomposed by anaerobic bacteria, they decompose and generate a bad odor, etc. Therefore, decomposition by aerobic bacteria is suitable.
【0003】[0003]
【発明が解決しようとする課題】従って、従来のこの種
の処理装置においては、どのような効果的な前処理を施
すか或いは如何にして好気的環境を維持するかが成否の
鍵となっていた。本発明は、このような課題を解決する
ものであり、固液分離した液状分を微生物の作用で分解
処理するにつき、好気性微生物の生育環境を高めてその
分解力を高めたものである。Therefore, in the conventional processing apparatus of this kind, what effective pretreatment or how to maintain the aerobic environment is the key to success or failure. Was there. The present invention is intended to solve such a problem and to enhance the growth environment of aerobic microorganisms and enhance their decomposing power when the solid-liquid separated liquid component is decomposed by the action of microorganisms.
【0004】[0004]
【課題を解決するための手段】この課題の下、本発明
は、請求項1に記載した、家畜糞尿を固液分離してそれ
ぞれ微生物の作用で分解処理する家畜糞尿処理装置にお
いて、液状分を分解処理する分解槽を複数設け、分解槽
の上流側にミネラル分が含まれる生命活性化液が加えら
れる第一曝気槽を設けるとともに、下流側に表面を磨い
たカキ殻を浸漬した仕上槽を設けたことを特徴とする家
畜糞尿処理装置を提供したものである。Under the above problems, the present invention provides a livestock excrement treating apparatus for solid-liquid separating livestock excrement according to claim 1 and decomposing the same by the action of microorganisms. providing a plurality of decomposition vessel to decompose, provided with a first aeration tank which life activating solution containing the minerals on the upstream side of the decomposition vessel is added, a finish bath immersion oyster shells polished surface on the downstream side The present invention provides a livestock excrement treatment device characterized by being provided.
【0005】又、本発明は、請求項4に記載した、家畜
糞尿を固液分離してそれぞれ微生物の作用で分解処理す
る家畜糞尿処理装置による家畜糞尿処理方法であって、
液状分を分解処理する分解槽を複数設け、分解槽の上流
側の第一曝気槽にミネラル分が含まれる生命活性化液を
加えて微生物作用を活発化させ、下流側の仕上槽内に表
面を磨いたカキ殻を浸漬して微生物の生育床としたこと
を特徴とする家畜糞尿処理装置よる家畜糞尿処理方法を
提供する。The present invention also provides a livestock excrement treating method using a livestock excrement treating apparatus for solid-liquid separating livestock excrement and decomposing it by the action of microorganisms.
A plurality of decomposition tanks for decomposing liquid components are provided, and a bioactive liquid containing minerals is added to the first aeration tank on the upstream side of the decomposition tank to activate the microbial action , and the surface in the finishing tank on the downstream side. A method for treating livestock excrement by a livestock excrement treating apparatus, which comprises immersing a polished oyster shell as a microbial growth bed.
【0006】液状分の曝気過程において、ミネラル分を
含む生命活性化液を加えると、そのミネラル分が嫌気性
菌の活動を抑えて液状分を腐り難くするとともに、好気
性菌の栄養分となって繁殖を促す。更に、このミネラル
分は、空気中の波動エネルギーを吸収して液状分を活性
化するとも言われている。更に、分解槽の下流側を構成
する仕上槽に表面を磨いたカキ殻を浸漬すると、カキ殻
に形成された微小孔が微生物の絶好の生育床となり、そ
の繁殖を促して分解を促進する。[0006] In the aeration process of the liquid content, the addition of life activation liquid containing minerals, together with the mineral is less likely to rot the liquid content by suppressing the activity of anaerobic bacteria become nutrients aerobes Encourage breeding. Further, it is said that this mineral component absorbs wave energy in the air to activate the liquid component. Furthermore, when the oyster shell with a polished surface is immersed in a finishing tank constituting the downstream side of the decomposition tank, the micropores formed in the oyster shell serve as a perfect growth bed for microorganisms, promoting their growth and promoting decomposition.
【0007】以下、本発明の実施の形態を図面を参照し
て説明する。図1は本発明の一例を示す分解処理装置の
配置及びフロー図であるが、畜舎から出た糞尿はひとま
ず地下タンク1等に水を加えて貯留しておく。これをポ
ンプ2で汲み上げて固液分離器3に送り、ここで固形分
4と液状分5とに分ける。このうちの固形分4は堆肥に
するのであるが、それには、コンベア6等で堆肥舎7に
送り、適宜ショベル8等で切返しを行って発酵させる。
発酵して堆肥9となったものは、トラック10等で希望
農家に搬送したり、ストックヤード11で保管する。Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a layout and flow diagram of a decomposition treatment apparatus showing an example of the present invention. Manure discharged from a livestock barn is temporarily stored by adding water to an underground tank 1 or the like. This is pumped up by the pump 2 and sent to the solid-liquid separator 3, where it is separated into a solid content 4 and a liquid content 5. Of these, the solid content 4 is made into compost, which is sent to the compost house 7 by the conveyor 6 or the like and appropriately turned by the shovel 8 or the like to ferment it.
The fermented compost 9 is transported to a desired farm by a truck 10 or the like, or stored in the stockyard 11.
【0008】一方、液状分5については、一旦貯留槽1
2に集め、ここに水中ミキサー13で適宜攪拌しながら
溜めておく。これをポンプ14で分解槽15に送り、こ
こで分解するのであるが、本例における分解槽15は、
上流側から第一曝気槽16、第二曝気槽17、沈澱槽1
8、仕上槽19で構成されている。第一及び第二曝気槽
16、17による分解は、この中にブロワ20で空気を
送りながら液状分5を空気と接触させ、好気性菌の作用
で分解を行うものである。On the other hand, the liquid content 5 is once stored in the storage tank 1.
2 and collect them in the underwater mixer 13 with appropriate stirring. This is sent to the decomposition tank 15 by the pump 14 and decomposed here. The decomposition tank 15 in this example is
From the upstream side, the first aeration tank 16, the second aeration tank 17, the precipitation tank 1
8 and finishing tank 19. Decomposition by the first and second aeration tanks 16 and 17 is carried out by sending air through the blower 20 to bring the liquid component 5 into contact with air and performing decomposition by the action of aerobic bacteria.
【0009】本発明の特徴の一つは、最初の分解槽15
である第一曝気槽16にミネラル分を含む生命活性化液
21を加えることである。このミネラル分の添加によ
り、嫌気性菌の活動を抑えて液状分5を腐り難くすると
ともに、これが好気性菌の栄養分となって繁殖を促す。
更に、このミネラル分は、空気中の波動エネルギーを吸
収して液状分5を活性化する。 One of the features of the present invention is that the first decomposition tank 15 is used.
It is to add life activating liquid 21 containing minerals to the first aeration tank 16 is. The addition of this mineral component suppresses the activity of anaerobic bacteria and makes the liquid component 5 less prone to decay, and serves as nutrients for aerobic bacteria to promote reproduction.
In addition, the minerals are you activate liquid content of 5 to absorb the wave energy in the air.
【0010】第一曝気槽16で分解された液状分5は、
第二曝気槽17に移され、ここでも分解を継続されつ
つ、沈澱槽18に移される。尚、これらの移送は、溢流
や流下による自然移送でもよいし、ポンプ等で加圧する
強制移送でもよい。沈澱槽18に移された液状分5は、
その汚泥成分が底に溜まるから、これをポンプ22で第
一曝気槽16に還元し、分解を繰り返す。The liquid component 5 decomposed in the first aeration tank 16 is
It is moved to the second aeration tank 17 and is moved to the precipitation tank 18 while continuing to be decomposed here. The transfer may be natural transfer by overflow or downflow, or forced transfer by pressurizing with a pump or the like. The liquid content 5 transferred to the settling tank 18 is
Since the sludge component collects at the bottom, it is returned to the first aeration tank 16 by the pump 22, and the decomposition is repeated.
【0011】沈澱槽18内の液状分5は、仕上槽19に
移され、ここで仕上げ処理される。この仕上げ処理も、
ブロワ20で仕上槽19内に空気を送り(23は圧力ス
イッチ)、好気性菌による好気分解であるが、本発明で
は、この仕上槽19にカキ殻24を浸漬してこれで分解
を促進させるのである。The liquid component 5 in the settling tank 18 is transferred to a finishing tank 19 where it is finished. This finishing process also
The blower 20 sends air into the finishing tank 19 (23 is a pressure switch) for aerobic decomposition by aerobic bacteria. In the present invention, the oyster shell 24 is immersed in the finishing tank 19 to promote decomposition. Let them do it.
【0012】図2はカキ殻24の斜視図であるが、ここ
で使用するカキ殻24は、その表面(表面及び裏面)を
磨いて表面に付いている海藻や泥を完全に落とすことが
肝要である。カキ殻24の表面には微小な孔が数多く形
成されており、これが微生物の生育床となるのである
が、海藻や泥が付いたままでは、孔が塞がってこの生育
床効果が十分に発揮されないからである。FIG. 2 is a perspective view of the oyster shell 24. It is essential that the surface (front and back) of the oyster shell 24 used here is polished to completely remove seaweed and mud attached to the surface. Is. Many micropores are formed on the surface of the oyster shell 24, and this serves as a growth bed for microorganisms. However, if seaweed or mud remains, the pores will be blocked and the growth bed effect will not be sufficiently exerted. Because.
【0013】図3はカキ殻24の浸漬状態を示す説明図
であるが、以上のカキ殻24を適当な網袋25に収納
し、これを仕上槽19内に吊るしておけばよい。このと
きに用いるカキ殻24の量は適宜でよいが、多い方が生
育床が増えて微生物の活動が活発になる。尚、カキ殻2
4は、炭酸カルシウムを主体としており、微生物の活動
によって溶解し、その量を減ずるから、減じた分だけ適
当に補充すればよい。FIG. 3 is an explanatory view showing how the oyster shells 24 are immersed, but the above oyster shells 24 may be housed in a suitable net bag 25 and hung in the finishing tank 19. The amount of the oyster shells 24 used at this time may be arbitrary, but the larger the number, the more the growth bed and the more active the microorganisms. In addition, oyster shell 2
4 is mainly composed of calcium carbonate, which is dissolved by the activity of microorganisms and its amount is reduced, so that it is sufficient to supplement the reduced amount appropriately.
【0014】このような分解を継続して行くと、液状分
5は、最終的には無害化された炭酸ガスと水とに分解さ
れるから、その水分をポンプ26で汲み上げ、農地等に
還元すればよい。又、最初の地下タンク1に戻し、添加
する水の増量剤又は代わりとしてもよい。When such decomposition is continued, the liquid content 5 is finally decomposed into detoxified carbon dioxide gas and water. Therefore, the water content is pumped up by the pump 26 and returned to farmland or the like. do it. Further, it may be returned to the first underground tank 1 and used as a filler or substitute for water to be added.
【0015】[0015]
【発明の効果】以上、本発明によれば、家畜糞尿の液状
分を処理するに際して生命活性化液の添加やカキ殻の使
用によって好気分解が短時間でより完全に行われる。従
って、設備を大掛かりにする必要はなく、低コストで省
スペースのものができる。As described above, according to the present invention, aerobic decomposition is completed more completely in a short time by adding a life activation liquid or using oyster shells when treating a liquid content of livestock excrement. Therefore, it is not necessary to large-scale equipment, it is that of space at a low cost.
【図面の簡単な説明】[Brief description of drawings]
【図1】本発明の一例を示す家畜糞尿処理装置の配置及
びフロー図である。FIG. 1 is a layout and flow diagram of a livestock manure processing apparatus showing an example of the present invention.
【図2】本発明の一例を示すカキ殻の斜視図である。FIG. 2 is a perspective view of an oyster shell showing an example of the present invention.
【図3】本発明の一例を示すカキ殻を網袋に詰めた状態
の説明図である。FIG. 3 is an explanatory diagram showing a state in which an oyster shell according to an example of the present invention is packed in a net bag.
【符号の説明】 15 分解槽 16 第一曝気槽 19 仕上槽 21 生命活性液 24 カキ殻 25 網袋[Explanation of symbols] 15 Decomposition tank 16 First aeration tank 19 finishing tank 21 bioactive liquid 24 oyster shells 25 mesh bag
Claims (4)
の作用で分解処理する家畜糞尿処理装置において、液状
分を分解処理する分解槽を複数設け、分解槽の上流側に
ミネラル分が含まれる生命活性液が加えられる第一曝気
槽を設けるとともに、下流側に表面を磨いたカキ殻を浸
漬した仕上槽を設けたことを特徴とする家畜糞尿処理装
置。1. A livestock manure processing apparatus for solid-liquid separating livestock manure and decomposing it by the action of microorganisms, wherein a plurality of decomposing tanks for decomposing liquid components are provided, and minerals are contained on the upstream side of the decomposing tanks. A livestock excrement treatment apparatus, characterized in that a first aeration tank to which a bioactive liquid is added is provided, and a finishing tank in which a polished oyster shell is immersed is provided on the downstream side.
ある請求項1の家畜糞尿処理装置。2. The livestock excrement treatment device according to claim 1, wherein the bioactivation liquid contains deep sea water.
り下げられるものである請求項1又は2の家畜糞尿処理
装置。3. The livestock manure processing device according to claim 1 or 2, wherein the oyster shells are packed in a net bag and suspended in a treatment tank.
の作用で分解処理する家畜糞尿処理装置による家畜糞尿
処理方法であって、液状分を分解処理する分解槽を複数
設け、分解槽の上流側の第一曝気槽にミネラル分が含ま
れる生命活性化液を加えて微生物作用を活発化させ、下
流側の仕上槽に表面を磨いたカキ殻を浸漬して微生物の
生育床としたことを特徴とする家畜糞尿処理装置よる家
畜糞尿処理方法。4. A livestock manure processing method using a livestock manure processing device for solid-liquid separating livestock manure and decomposing it by the action of microorganisms, wherein a plurality of decomposition tanks for decomposing liquid components are provided, and an upstream of the decomposition tank. The vitalizing liquid containing minerals was added to the first aeration tank on the side to activate the microbial action, and the oyster shell whose surface was polished was immersed in the finishing tank on the downstream side to form a microbial growth bed. A method for treating livestock manure by a characteristic livestock manure treatment device.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2002029187A JP2003225696A (en) | 2002-02-06 | 2002-02-06 | Apparatus for treating excreta of domestic animal and method for treating excreta of domestic animal by using the apparatus |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2002029187A JP2003225696A (en) | 2002-02-06 | 2002-02-06 | Apparatus for treating excreta of domestic animal and method for treating excreta of domestic animal by using the apparatus |
Publications (1)
Publication Number | Publication Date |
---|---|
JP2003225696A true JP2003225696A (en) | 2003-08-12 |
Family
ID=27750059
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2002029187A Pending JP2003225696A (en) | 2002-02-06 | 2002-02-06 | Apparatus for treating excreta of domestic animal and method for treating excreta of domestic animal by using the apparatus |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2003225696A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPWO2006057287A1 (en) * | 2004-11-25 | 2008-06-05 | 楠 敏明 | Activated sludge production inhibitor |
CN100441522C (en) * | 2005-08-02 | 2008-12-10 | 马守祥 | Oyster case active filtering material for sewage treatment and preparation method thereof |
JP2009247956A (en) * | 2008-04-03 | 2009-10-29 | Sekisui Chem Co Ltd | Livestock feces and urine transporting system |
-
2002
- 2002-02-06 JP JP2002029187A patent/JP2003225696A/en active Pending
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPWO2006057287A1 (en) * | 2004-11-25 | 2008-06-05 | 楠 敏明 | Activated sludge production inhibitor |
CN100441522C (en) * | 2005-08-02 | 2008-12-10 | 马守祥 | Oyster case active filtering material for sewage treatment and preparation method thereof |
JP2009247956A (en) * | 2008-04-03 | 2009-10-29 | Sekisui Chem Co Ltd | Livestock feces and urine transporting system |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Imbeah | Composting piggery waste: a review | |
Tritt et al. | Materials flow and possibilities of treating liquid and solid wastes from slaughterhouses in Germany. A review | |
Sinha et al. | Sewage treatment by vermifiltration with synchronous treatment of sludge by earthworms: a low-cost sustainable technology over conventional systems with potential for decentralization | |
Salminen et al. | Anaerobic digestion of organic solid poultry slaughterhouse waste–a review | |
CA2428417C (en) | Low oxygen organic waste bioconversion system | |
Chávez-Fuentes et al. | Manure from our agricultural animals: A quantitative and qualitative analysis focused on biogas production | |
JP4384141B2 (en) | How to use recycled water | |
Chynoweth et al. | Anaerobic treatment of piggery slurry-review | |
Pungrasmi et al. | Nitrogen removal from a recirculating aquaculture system using a pumice bottom substrate nitrification-denitrification tank | |
WO2012034118A2 (en) | Process for the treatment of biological materials and wastewater | |
Choi | Piggery waste management | |
CN206553279U (en) | Microorganism in situ alternative amplification device | |
CN111842419B (en) | Kitchen waste treatment method | |
JP2003225696A (en) | Apparatus for treating excreta of domestic animal and method for treating excreta of domestic animal by using the apparatus | |
JP2006212612A (en) | Method for decomposing and extinguishing excrement and urine of hog raising using composite fermentation method in composite microorganism dynamic system analysis of composite microorganism system | |
Abeliovich | Water pollution and bioremediation by microalgae: Water purification: Algae in wastewater oxidation ponds | |
JP2695610B2 (en) | Fish and shellfish cultivation method using purified livestock wastewater | |
JPH06134474A (en) | Activated water tank for feeding livestock and poultry | |
JP4866595B2 (en) | Method and apparatus for treating deposits such as shellfish | |
JP2005328735A (en) | Method for culturing fishes or shellfishes and fish or shellfish-culturing apparatus used for the method | |
JP3299806B2 (en) | Wastewater treatment method | |
CN220116327U (en) | Device for promoting diversification of water body habitat of circulating water culture pond | |
JP2005160418A (en) | System for treating dung and urine of animal | |
Dar et al. | Intrusion of Biotechnology for Degradation of Organic Wastes | |
JP2022066374A (en) | Denitrification device, denitrification method, and water treatment system using denitrification device |