JP2007284332A - Method and apparatus for producing compost raw material - Google Patents

Method and apparatus for producing compost raw material Download PDF

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JP2007284332A
JP2007284332A JP2006142044A JP2006142044A JP2007284332A JP 2007284332 A JP2007284332 A JP 2007284332A JP 2006142044 A JP2006142044 A JP 2006142044A JP 2006142044 A JP2006142044 A JP 2006142044A JP 2007284332 A JP2007284332 A JP 2007284332A
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tank
aeration
pump
composting
mixing tank
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Katsuhisa Tokuda
勝寿 徳田
Seiichiro Murayama
精一郎 村山
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SANWA ONCHO KOGYO KK
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SANWA ONCHO KOGYO KK
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    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy
    • 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
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Abstract

<P>PROBLEM TO BE SOLVED: To provide a means for producing a compost raw material, composting the raw material in a short term and capable of adjusting its pH at a low cost. <P>SOLUTION: The apparatus is one provided with means for throwing the contents in an aeration tank 1 and in a sludge storage tank 4 into a mixing tank 5, a cutter-fitted submerged filth pump 22 provided in the lower part of a storage tank 21, and a submerged filth pump 28 provided in the lower part of a mixing tank 27, and agitators 23, 29, and 34 provided in the storage tank 21, the mixing tank 27, and a coagulation tank 33 respectively, wherein a connection is made between the discharge port of the cutter-fitted submerged filth pump 22 and the upper part of the mixing tank 27, a connection is made between the discharge port of the submerged filth pump 28 and the upper part of the coagulation tank 33, connections are made between the discharge port of a blower 39 of an additive tank 38 and the upper part of the mixing tank 27 and between the discharge port of a chemical injection pump 37 and the upper part of the coagulation tank 33, and connections are made between the inlet of a screw press 41 and the lower part of the coagulation tank 33, between the bottom of the mixing tank 5 and the upper part of the storage tank 21, and between the supernatant liquor discharge port 43 of the screw press 41 and the aeration tank 1. <P>COPYRIGHT: (C)2008,JPO&INPIT

Description

この発明は、家畜糞尿や下水その他の汚泥そして食品残さ物などを、ペーハー調整手段を用いつつ、木質繊維と高分子凝集剤を用いてコンポスト化用原料を製造する方法とその装置に関する。  The present invention relates to a method and apparatus for producing raw materials for composting of animal manure, sewage and other sludge and food residues using wood fiber and a polymer flocculant while using pH adjusting means.

従来より、コンポスト化用原料を製造するための種々の方法・装置が利用されているが、本発明にて示すように、ペーハー調整を行いつつ木質繊維と高分子凝集剤の双方を用いる手段は現在のところ見当たらない。  Conventionally, various methods and apparatuses for producing composting raw materials have been used, but as shown in the present invention, means for using both wood fibers and a polymer flocculant while adjusting pH I can't find it right now.

以前より、コンポスト(堆肥、とくに都市ゴミや汚泥などから作った堆肥)が多用されている。家畜糞尿や各種汚泥等の中には発酵により飼料化や肥料化が可能な成分が多量に含まれているため、コンポスト原料として利用する試みはこれまでにも多くなされている。
しかし、コンポスト化に際しては原料の含水率が重要なファクターである。
含水率80%以上では通気度が低く、嫌気発酵および腐敗による著しい腐敗臭・悪臭が生じ、堆肥等を生成するために必要な発酵が行われない。そのため、この含水率を65%以下にする必要があるが、各種汚泥等の含水率は90%以上であり、そのままではコンポスト化原料としては使用不能である。それゆえに各種汚泥等をコンポスト化するために、わら、籾殻、おがくず等を汚泥に加えて含水率を低下する手段も用いられているが、汚泥量に対し2〜3倍程度加えることとなるため、処理体積の増大による発酵タンク容積の大型化が必要となる。また、発酵速度の速い汚泥と遅いわら、籾殻、おがくずの間でアンバランスが生じ、これからコンポスト化すると未完熟の肥料が生成されることとなる。
他方、各種汚泥等を高熱炉で乾燥して含水率を下げることも行われているが、コスト高となり、75%以下の含水率は得難いものである。
さらに、古紙の吸水性を利用して、これを汚泥に加えて加圧脱水する手段もあるが、この手段では含水率を70%以下にするためには古紙を40%以上加えなければならず、また前記のような完熟度のアンバランスが生じてやはり未完熟の肥料となるものである。
この未完熟の肥料が土中に入ると、土壌中での酸素欠乏や脱リン現象が発生し、農作物栽培にとって障害を引き起こす原因となるものであった。
他方、コンポスト化原料製造にあたっては生成される脱水ケーキのペーハー値が問題である。つまり、既述の家畜糞尿や下水その他の汚泥そして食品残さ物などはペーハー値が低い、すなわち酸性に傾いている場合が多く、これをそのまま用いてコンポスト原料を製造すると、製造工程に必要な固液分離がしにくく、また発酵微生物が働かないものとなってコンポスト原料としては好ましくない。これらを解決するために、従来はアルカリ性物質である消石灰を必要に応じて汚泥等に混入することにより、ペーハー値の調整を行っていた。しかし、これはコストアップにつながり、より効率よくペーハー調整のできる手段が求められている。
本発明は、以上のような従来からのコンポスト化原料の製造に関わる課題を解決するために発明されたもので、汚泥等にペーハー調整を行うとともに木質繊維と高分子凝集剤を添加して攪拌し、加圧脱水することによって好適なるコンポスト化用原料を得るための手段を提供することを目的として開発されたものである。
Compost (compost, especially compost made from municipal waste and sludge) has been used frequently. Since livestock manure and various sludges contain a large amount of components that can be made into feed or fertilizer by fermentation, many attempts have been made to use them as compost raw materials.
However, the moisture content of the raw material is an important factor in composting.
When the water content is 80% or more, the air permeability is low, and anaerobic fermentation and significant odor and malodor caused by rot occur, and fermentation necessary for producing compost and the like is not performed. Therefore, the water content needs to be 65% or less, but the water content of various sludges is 90% or more and cannot be used as a composting raw material as it is. Therefore, in order to compost various sludge, etc., means to reduce the water content by adding straw, rice husk, sawdust etc. to the sludge is also used, but it will add about 2 to 3 times the amount of sludge Therefore, it is necessary to increase the volume of the fermentation tank by increasing the processing volume. Moreover, imbalance occurs between sludge having a high fermentation rate and slow straw, rice husks, and sawdust, and when composted from this, unripe fertilizer is produced.
On the other hand, various sludges and the like are dried in a high-heat furnace to lower the water content, but the cost is high and it is difficult to obtain a water content of 75% or less.
In addition, there is a means for adding water to the sludge and dehydrating under pressure by utilizing the water absorption of the waste paper. However, in order to reduce the water content to 70% or less, it is necessary to add 40% or more of the waste paper. In addition, an imbalance of the degree of maturity as described above occurs, and the fertilizer is still unripe.
When this immature fertilizer enters the soil, oxygen deficiency and dephosphorization occur in the soil, causing damage to crop cultivation.
On the other hand, the pH value of the dehydrated cake produced is a problem when composting raw materials are produced. In other words, livestock manure, sewage and other sludge and food residues described above often have a low pH value, i.e., are inclined to acidity. Liquid separation is difficult and fermentation microorganisms do not work, which is not preferable as a compost raw material. In order to solve these problems, conventionally, the pH value is adjusted by mixing slaked lime, which is an alkaline substance, into sludge as required. However, this leads to an increase in cost, and there is a need for a means that enables more efficient pH adjustment.
The present invention was invented in order to solve the conventional problems relating to the production of composting raw materials as described above, and was adjusted by adding pH to the sludge and adding a wood fiber and a polymer flocculant and stirring. However, it was developed for the purpose of providing means for obtaining a suitable composting raw material by dehydrating under pressure.

課題を解決する手段として本発明は、以下の製造方法と製造装置に構成した。すなわち、
1.脱離液をエアレーションする第一工程。
2.エアレーション後の脱離液にコンポスト化対象物を混入する第二工程。
3.混入後の液に必要に応じて適宜に消石灰を投入する第三工程。
4.第三工程で得られた液に木質繊維を加えて攪拌する第四工程。
5.木質繊維添加攪拌後の物質に高分子凝集剤を加えて攪拌する第五工程。
6.高分子凝集剤添加攪拌後の物質を圧搾・脱水する第六工程。
7.第六工程で得られた脱離液を第一工程に戻してエアレーションする第七工程。
本発明の一つは、以上の各工程からなることを特徴とするコンポスト化用原料の製造方法である。
また、本発明の他の一つは、
エアレーション機能を備えたエアレーションタンクと、汚泥貯留タンクと、混入タンクを各々設け、エアレーションタンクと汚泥貯留タンクの貯留物を混入タンクへ投入する手段を設け、一方、適宜形状・サイズの中空体による貯留槽、混合槽、凝集槽、添加剤タンク、薬剤タンクを各々設け、貯留槽内下部にカッター付き水中汚物ポンプ、混合槽内下部に水中汚物ポンプを各々設置し、貯留槽と混合槽および凝集槽に、羽根を有し槽の上方から下方に向かう回転軸を回転させるモーターを有する攪拌機を各々設け、薬剤タンクに薬注ポンプ、添加剤タンクにブロワーを各々設け、前記カッター付き水中汚物ポンプの吐出口と混合槽の上部、水中汚物ポンプの吐出口と凝集槽上部を各々配管接続するとともに、ブロワー吐出口と混合槽上部、薬注ポンプ吐出口と凝集槽上部を各々配管接続し、一方、スクリュープレス機を設けるとともに該スクリュープレス機の入り口と凝集槽下部を配管接続し、前記の混入タンク底部と貯留槽上部を配管接続し、スクリュープレス機の脱離液排出口とエアレーションタンクを配管接続し、必要に応じ各配管途中にポンプを位置させ、各電動機器への通電制御システムを設けることにより、投入されたコンポスト化対象物のペーハー調整を行い、攪拌し、木質繊維を加えて攪拌し、さらに高分子凝集剤を加えて攪拌後、圧搾・脱水してコンポスト化用原料を製造するとともに、この脱水して得られる脱離液を再びエアレーションして再利用することにより、低コストでのペーハー調整と適正保水率のコンポスト化用原料が得られるよう構成したことを特徴とするコンポスト化用原料の製造装置である。
As means for solving the problems, the present invention is constituted by the following manufacturing method and manufacturing apparatus. That is,
1. The first step of aerating the desorbed liquid.
2. A second step in which the composting target is mixed into the desorbed liquid after aeration.
3. A third step in which slaked lime is appropriately added to the mixed liquid as necessary.
4). A fourth step of adding wood fiber to the liquid obtained in the third step and stirring.
5). The fifth step of adding and stirring the polymer flocculant to the substance after the addition of the wood fiber.
6). Sixth step of squeezing and dewatering the material after adding and stirring the polymer flocculant.
7). A seventh step of returning the desorbed liquid obtained in the sixth step to the first step and aeration.
One aspect of the present invention is a method for producing a composting raw material comprising the above steps.
Another aspect of the present invention is:
An aeration tank with an aeration function, a sludge storage tank, and a mixing tank are provided, and a means for introducing the aeration tank and sludge storage tank into the mixing tank is provided. A tank, a mixing tank, a coagulation tank, an additive tank, and a chemical tank are provided, an underwater waste pump with a cutter is installed in the lower part of the storage tank, and an underwater waste pump is installed in the lower part of the mixing tank. In addition, a stirrer having a blade and a motor for rotating a rotating shaft from the upper side to the lower side of the tank is provided, a chemical injection pump is provided in the drug tank, and a blower is provided in the additive tank, respectively. Connect the outlet and the upper part of the mixing tank, the discharge port of the submersible waste pump and the upper part of the coagulation tank, respectively, the blower discharge port and the upper part of the mixing tank, Note: The pump discharge port and the upper part of the coagulation tank are connected by piping, while a screw press machine is provided, the inlet of the screw press machine and the lower part of the coagulation tank are connected by piping, and the bottom of the mixing tank and the upper part of the storage tank are connected by piping. The connected composting object is established by connecting the release port of the screw press machine and the aeration tank by piping, positioning the pump in the middle of each piping as necessary, and providing a power supply control system for each electric device. After adjusting the pH of the mixture, stirring, adding the wood fiber, stirring, further adding the polymer flocculant, stirring, pressing and dewatering to produce a composting raw material, the desorption obtained by this dehydration It was configured to obtain a raw material for composting with low-cost pH adjustment and proper water retention by re-aeration and reuse of the liquid An apparatus for producing compost raw material, characterized.

本発明によれば、低コストでのコンポスト化用原料のペーハー調整が可能であるとともに、吸水性が高くかつ投入物と同等の発酵時間を有する木質繊維と、安全性の高いカチオン性天然高分子凝集剤を用いて攪拌・脱水処理を行うので、適度な含水率の脱水ケーキが得られ、これを用いて短期間でのコンポスト化を可能とする新規かつ有用なるコンポスト化用原料を得るための手段を得ることができる。  According to the present invention, it is possible to adjust the pH of a composting raw material at a low cost, and the wood fiber having a high water absorption and a fermentation time equivalent to the input material, and a highly safe cationic natural polymer Since the flocculant is used for agitation and dehydration treatment, a dehydrated cake with an appropriate water content can be obtained, and this can be used to obtain a new and useful composting raw material that enables composting in a short period of time. Means can be obtained.

以下、本発明の実施形態について説明する。
図において、1はエアレーションタンクで、上部開放有底円筒体である。2はエアーコンプレッサー、3は送気管である。この送気管はエアーコンプレッサーに接続され、他端は該タンク上方から下降してタンク内底部近傍に位置する。4は汚泥貯留タンク、5は混入タンクで、前記エアレーションタンクと同様構成である。6は脱離液移送管で、その一端はエアレーションタンク底部に取り付けられ、他端は混入タンク上部から下降してタンク内に位置する。7は脱離液送水ポンプで、脱離液移送管適所に設けられる。
8は汚泥移送管で、その一端は汚泥貯留タンク底部に取り付けられ、他端は混入タンク上部を通ってタンク内に位置する。9は汚泥移送ポンプで、汚泥移送管適所に設けられる。
10は混合液移送管で、その一端は混入タンク底部に接続され、他端は後述の貯留槽上部に位置する。11は混合液移送ポンプで、混合液移送管に設けられる。12は脱離液投入管で、その一端はエアレーションタンク上部を通ってタンク内に位置し、他端は、後述のスクリュープレス機の脱離液排出口に接続される。13は脱離液移送ポンプで、脱離液投入管適所に設けられる。以上がペーハー調整のための装置部である。
次ぎにコンポスト化原料製造のための装置部について説明する。
図において、21は貯留槽で、金属製の有底中空円筒体で、その内底にカッター付き水中汚物ポンプ22が設置される。23はモーター駆動による攪拌機で、貯留槽上部に適宜支持部材(図示略)にて設けられる箱体内に位置し、その下方に回転軸24が延びてこの回転軸適所に羽根25が取り付けられている。26は液面制御電極棒で、貯留槽上部にその本体部分が位置し、貯留槽内下方に向けて電極部分が延びている。この液面制御電極棒は、長さの異なる3本のステンレス棒を有し、それぞれの棒下端の液面接触にて液面位置を感知し、信号を発するものである。
27は貯留槽と同様構成による混合槽で、その内底部には水中汚物ポンプ28が設置され、攪拌機29と液面制御電極棒30が同様に設けられる。
31は流量調整槽で、中空直方体であり、その内面には長方形板体を上下交互に固着してなる邪魔板32が位置している。33は混合槽と同様構成による凝集槽で、同様に攪拌機34および液面制御電極棒35が設けられる。
36は薬剤タンクで中空直方体形状であり、その上部には薬注ポンプ37が位置している。38は添加剤タンクで、中空円筒体の下部に逆円錐形部分を一体に形成した形状であり、その下部にはブロワー39が位置する。40はフロック槽で、中空直方体である。
41はスクリュープレス機である。このスクリュープレス機は円筒ストレーナ内で特殊スクリューを回転させて内容物を圧搾・移送しながら連続脱水するものであり、脱水後は脱水ケーキが排出口42より排出され、脱離液が排出口43に接続されている脱離液投入管12を経てエアレーションタンク内に投入される。
Hereinafter, embodiments of the present invention will be described.
In the figure, reference numeral 1 denotes an aeration tank, which is an upper open bottomed cylindrical body. 2 is an air compressor, 3 is an air pipe. The air supply pipe is connected to an air compressor, and the other end descends from above the tank and is located near the bottom of the tank. 4 is a sludge storage tank and 5 is a mixing tank, which has the same configuration as the aeration tank. 6 is a desorption liquid transfer pipe, one end of which is attached to the bottom of the aeration tank, and the other end is lowered from the upper part of the mixing tank and is located in the tank. Desorption liquid water pump 7 is provided at an appropriate position in the desorption liquid transfer pipe.
8 is a sludge transfer pipe, one end of which is attached to the bottom of the sludge storage tank, and the other end is located in the tank through the upper part of the mixing tank. Reference numeral 9 denotes a sludge transfer pump, which is provided at an appropriate place in the sludge transfer pipe.
Reference numeral 10 denotes a mixed liquid transfer pipe, one end of which is connected to the bottom of the mixing tank and the other end is located at the upper part of the storage tank described later. 11 is a mixed liquid transfer pump, and is provided in the mixed liquid transfer pipe. Reference numeral 12 denotes a detachment liquid input pipe, one end of which is located in the tank through the upper part of the aeration tank, and the other end is connected to a detachment liquid discharge port of a screw press machine described later. Desorption liquid transfer pump 13 is provided at an appropriate position of the desorption liquid input pipe. The above is the apparatus unit for pH adjustment.
Next, the apparatus part for manufacturing the composting raw material will be described.
In the figure, reference numeral 21 denotes a storage tank, which is a metal bottomed hollow cylindrical body, and an underwater filth pump 22 with a cutter is installed on the inner bottom thereof. Reference numeral 23 denotes a motor-driven stirrer, which is positioned inside a box provided with a support member (not shown) as appropriate in the upper part of the storage tank. . 26 is a liquid level control electrode rod, the main body part is located in the upper part of a storage tank, and the electrode part is extended toward the downward direction in a storage tank. This liquid level control electrode rod has three stainless steel rods having different lengths, and senses the liquid level position by the liquid level contact at the lower end of each rod and generates a signal.
Reference numeral 27 denotes a mixing tank having the same configuration as the storage tank. An underwater filth pump 28 is installed at the inner bottom of the mixing tank, and a stirrer 29 and a liquid level control electrode rod 30 are similarly provided.
Reference numeral 31 denotes a flow rate adjusting tank, which is a hollow rectangular parallelepiped, and a baffle plate 32 formed by alternately adhering rectangular plate bodies to each other is located on the inner surface thereof. 33 is an agglomeration tank having the same configuration as the mixing tank, and is similarly provided with a stirrer 34 and a liquid level control electrode rod 35.
Reference numeral 36 denotes a medicine tank having a hollow rectangular parallelepiped shape, and a medicine injection pump 37 is positioned above the medicine tank. Reference numeral 38 denotes an additive tank having a shape in which an inverted conical portion is integrally formed at the lower portion of the hollow cylindrical body, and a blower 39 is positioned at the lower portion thereof. Reference numeral 40 denotes a flock tank, which is a hollow rectangular parallelepiped.
41 is a screw press machine. This screw press machine performs continuous dehydration while rotating and rotating the special screw in a cylindrical strainer, and after dehydration, the dehydrated cake is discharged from the discharge port 42 and the desorbed liquid is discharged from the discharge port 43. It is introduced into the aeration tank through the desorbed liquid introduction pipe 12 connected to.

以上の各装置は以下のように配管接続される。
カッター付き水中汚泥ポンプ22の吐出口と混合槽27の上部は攪拌物移送管50にて配管接続され、その中間に流量調整弁51が位置する。また、貯留槽内と混合槽内はオーバーフロー管52にて連通される。ブロワーの吐出口と混合槽内上部は添加剤移送管53にて接続される。混合槽内の水中汚物ポンプ28の吐出口と流量調整槽31は、流量調整弁54を介して一次混合移送管55にて接続され、また、混合槽上部と流量調整槽はオーバーフロー管56にて連通される。薬剤タンク上部の薬注ポンプの吐出口と凝集槽上部は薬注管57にて接続される。凝集槽下部とフロック槽側部は二次混合移送管58にて接続される。また、混合液移送管10は貯留槽21の上方から内部へ入り込み、ここから混合液が投入される。なお、各槽の上部は接続個所を除いて密閉もしくは蓋が設けられ、各モーターその他の電力使用機器には配線(図示略)にて電力供給がなされ、各機器を制御するための制御盤(図示略)が設けられる。また、図示の都合上、貯留槽位置は正規の位置に比べて上方に表現している。
Each of the above devices is connected by piping as follows.
The discharge port of the submersible sludge pump 22 with a cutter and the upper part of the mixing tank 27 are connected by a stirring material transfer pipe 50, and a flow rate adjusting valve 51 is located in the middle. Further, the inside of the storage tank and the inside of the mixing tank are communicated by an overflow pipe 52. The discharge port of the blower and the upper part in the mixing tank are connected by an additive transfer pipe 53. The discharge port of the submersible waste pump 28 in the mixing tank and the flow rate adjusting tank 31 are connected by a primary mixing transfer pipe 55 via a flow rate adjusting valve 54, and the upper part of the mixing tank and the flow rate adjusting tank are connected by an overflow pipe 56. Communicated. The discharge port of the chemical injection pump in the upper part of the chemical tank and the upper part of the coagulation tank are connected by a chemical injection pipe 57. The lower part of the agglomeration tank and the side part of the flock tank are connected by a secondary mixing transfer pipe 58. Further, the mixed liquid transfer pipe 10 enters the storage tank 21 from above, and the mixed liquid is supplied from here. In addition, the upper part of each tank is provided with a seal or lid except for connection points, and power is supplied to each motor and other power-using devices by wiring (not shown), and a control panel for controlling each device ( (Not shown) is provided. Further, for the convenience of illustration, the storage tank position is expressed above the regular position.

次ぎに本発明装置の使用について説明する。
まず、準備として添加剤タンクに添加剤としての微粉木質繊維を適量貯留する。
この木質繊維は間伐材や建築廃材を破砕機にて粗破砕し、さらに微粉破砕機にてパウダー状に砕いて得られる繊維質であり、黄色または黄褐色の物質である。
また、薬注タンク内に高分子凝集剤としてのカチオン性天然高分子凝集剤を貯留する。
次ぎに、あらかじめ用意した脱離液をエアレ−ションタンクに入れ、混入タンクに適量の消石灰を投入しておく。汚泥貯留タンクに汚泥等を汚泥投入管より投入し、エアーコンプレッサー駆動にてタンク内のエアレーションを行う。このエアレーションにて脱離液の濁度が改善され、液が安定化する。すなわち、嫌気発酵しにくく腐敗しにくくなり、混入汚泥の好気性菌の活性化がなされることとなる。
次ぎに、脱離液送水ポンプ7および汚泥移送ポンプ9を作動させることにて、エアレーション後の脱離液は脱離液移送管にて、汚泥は汚泥移送管にて各々混入タンクに投入される。この混入タンクにて汚泥と脱離液は自然対流にて混合し、混合液移送ポンプ作動にて混合液移送管を経て貯留槽へ処理後の液が投入される。この貯留槽内にて攪拌機による羽根回転にて4分〜6分程度の時間攪拌される。また、投入量制御のための液面制御電極棒が貯留槽に設けられており、この電極棒からの信号にて投入量を把握制御することができる。所定時間の攪拌後、カッター付き水中汚泥ポンプの下部から吸引された攪拌物は攪拌物移送管50を介して混合槽上部から槽内へ投入され、また、添加剤タンク内の木質繊維はブロワー39にて添加剤移送管53にて混合槽へ投入される。この木質繊維は攪拌物に対し、0.1〜10%(重量比)程度加えられる。この双方の材料は攪拌機29にて1〜2分間攪拌され、水中汚物ポンプ28にて吸引されて一次混合物移送管および流量調整槽を通過し、凝集槽へと送られる。なお、混合槽と貯留槽はオーバーフロー管52にて連通しており、余分な攪拌物は貯留槽へと戻される。流量調整槽には邪魔板が内設され、凝集槽への急激な移行を緩和している。
Next, the use of the device of the present invention will be described.
First, as preparation, an appropriate amount of fine wood fiber as an additive is stored in an additive tank.
This wood fiber is a fiber obtained by roughly crushing thinned wood or construction waste with a crusher and further crushing it into powder with a fine powder crusher, and is a yellow or tan substance.
In addition, a cationic natural polymer flocculant as a polymer flocculant is stored in the medicine tank.
Next, the prepared detachment liquid is put in the air tank, and an appropriate amount of slaked lime is put in the mixing tank. Sludge is introduced into the sludge storage tank through the sludge inlet pipe, and the tank is aerated by driving the air compressor. This aeration improves the turbidity of the desorbed liquid and stabilizes the liquid. That is, it becomes difficult to anaerobically ferment and it becomes difficult to rot, and the aerobic bacteria in the mixed sludge are activated.
Next, by operating the desorption liquid feed pump 7 and the sludge transfer pump 9, the desorption liquid after aeration is supplied to the mixing tank through the desorption liquid transfer pipe, and the sludge is input to the mixing tank through the sludge transfer pipe. . In this mixing tank, the sludge and the desorbed liquid are mixed by natural convection, and the processed liquid is charged into the storage tank through the mixed liquid transfer pipe by the mixed liquid transfer pump operation. The storage tank is stirred for about 4 to 6 minutes by rotating the blades with a stirrer. In addition, a liquid level control electrode rod for controlling the amount to be charged is provided in the storage tank, and the amount to be charged can be grasped and controlled by a signal from this electrode rod. After stirring for a predetermined time, the agitated material sucked from the lower part of the submersible sludge pump with a cutter is introduced into the tank from the upper part of the mixing tank via the agitated material transfer pipe 50, and the wood fiber in the additive tank is blower 39. Is added to the mixing tank through the additive transfer pipe 53. The wood fiber is added in an amount of about 0.1 to 10% (weight ratio) with respect to the stirred product. Both of these materials are stirred for 1 to 2 minutes by the stirrer 29, sucked by the underwater waste pump 28, passed through the primary mixture transfer pipe and the flow rate adjustment tank, and sent to the agglomeration tank. Note that the mixing tank and the storage tank communicate with each other through the overflow pipe 52, and excess agitated material is returned to the storage tank. A baffle plate is provided in the flow rate adjustment tank to mitigate rapid transition to the agglomeration tank.

木質繊維の添加攪拌後の物質は上記のように凝集槽に投入されるが、薬剤タンク内のカチオン性天然高分子凝集剤は薬注ポンプ37にて吸い上げられ、薬注管57を経て凝集槽へと送り出され、これら双方は攪拌機34にて4〜5分程度攪拌される。この攪拌にて次第にフロックが形成されてくる。このカチオン性天然高分子凝集剤は木質繊維添加攪拌物質に対し、0.01〜10%(重量比)程度の量が使用される。この凝集剤の添加攪拌後は、二次混合移送管58を経てフロック槽に一時貯留され、スクリュープレス機へと送られ、圧搾・脱水され、脱水ケーキは排出口42より排出され、脱離液は脱離液排出口43に接続されている脱離液投入管12にてエアレーションタンクに投入される。
この圧搾・脱水に要する時間は4〜7分間程度である。なお、混合槽および凝集槽は貯留槽同様に液面制御電極棒が備えられ、各槽の貯留量の管理が行われる。また、流量調整槽と混合槽間にはやはりオーバーフロー管56が連通しており、流量調整槽内の物質量が規制される。
このようにして得られた脱水ケーキは含水率65%以下となり、また、中性域のペーハーとなり、発酵ヤードにおいてコンポスト化され、堆肥や飼料の原料化を行うことができる。すなわち、通気性がよくなり、好気性菌による発酵が起こるので臭気も激減し、短期間によるコンポスト化が可能となる。
コンポスト化処理には水分の調整が重要であり、水分が70%以上になると好気性菌の作用により、有機物の分解のプロセスで二酸化炭素が発生して植物の根の機能を低下させて、硫化水素、アンモニア、メルカプタン等の有害ガスが発生し、農作物や環境に悪影響を及ぼすこととなる。従って、水分は65%以下を保つことが必要である。
通常、発酵ヤードにはコンポスト化促進のためにエアレーション装置を設け、外部空気を供給して発酵促進と脱臭を行うことにより、堆肥化の時間を短くすることができる。
このようにして通常のコンポスト化には3〜6ヶ月の期間を必要とするが、本発明によれば1〜3週間でコンポスト化を終了させることができ、得られたコンポスト肥料は農作物に対し有効に使用することができる。
The substance after the addition and stirring of the wood fiber is put into the coagulation tank as described above, but the cationic natural polymer coagulant in the chemical tank is sucked up by the chemical injection pump 37 and passes through the chemical injection pipe 57 to the coagulation tank. These are both stirred by the stirrer 4 for about 4 to 5 minutes. By this stirring, flocs are gradually formed. The cationic natural polymer flocculant is used in an amount of about 0.01 to 10% (weight ratio) with respect to the wood fiber-added stirring substance. After the addition and stirring of the flocculant, the floc tank is temporarily stored via the secondary mixing transfer pipe 58, sent to the screw press machine, pressed and dehydrated, and the dehydrated cake is discharged from the discharge port 42, and the desorbed liquid. Is introduced into the aeration tank through the desorbed liquid input pipe 12 connected to the desorbed liquid discharge port 43.
The time required for this compression / dehydration is about 4 to 7 minutes. In addition, the mixing tank and the agglomeration tank are provided with a liquid level control electrode rod like the storage tank, and the storage amount of each tank is managed. Further, an overflow pipe 56 is also communicated between the flow rate adjusting tank and the mixing tank, and the amount of substance in the flow rate adjusting tank is regulated.
The dehydrated cake thus obtained has a moisture content of 65% or less, becomes neutral pH, is composted in the fermentation yard, and can be used as a raw material for compost and feed. That is, the air permeability is improved and fermentation by aerobic bacteria occurs, so the odor is drastically reduced and composting in a short period is possible.
Moisture adjustment is important for composting treatment, and when the water content exceeds 70%, the action of aerobic bacteria causes carbon dioxide to be generated in the process of organic matter decomposition, reducing the function of plant roots and sulfidizing. Hazardous gases such as hydrogen, ammonia and mercaptans are generated, which adversely affects crops and the environment. Therefore, it is necessary to keep the moisture at 65% or less.
Usually, an aeration apparatus is provided in the fermentation yard for promoting composting, and the time for composting can be shortened by supplying external air to promote fermentation and deodorization.
Thus, although a period of 3 to 6 months is required for normal composting, according to the present invention, composting can be completed in 1 to 3 weeks, and the obtained compost fertilizer is applied to agricultural crops. It can be used effectively.

既述の手段により、脱水液と処理物とに分離したものが得られるが、この脱離液は投入物に比べてBOD(生物的酸素要求量)および浮遊汚泥が著しく低下しており、窒素含有量および燐含有量の低下も認められる。また、脱水物は、長さの異なったセルロースが立体的に縦横に絡み合った構造を有しており、吸湿・吸水性が高く、かつ放湿性が高いという特徴を有している。
本発明手段においては、木質繊維と高分子凝集剤の添加順序が重要であり、まず投入材料に木質繊維を添加し、攪拌してスラリーを形成させた後、高分子凝集剤を添加して攪拌することが必要で、この順序を逆にするとフロック(水と汚泥等の混合物)形成がなされず、期待する脱水効果は得られない。
なお、本発明に用いる木質繊維は、含水率15%程度となるように天日乾燥などを行ったものを用い、投入物の繊維含有量が多い場合には添加量を減らし、少ない場合には増やすなど状況に応じて加減して用い、木質繊維用として他に割り箸、古材チップ、わらなどの繊維材料を用いてもよい。また、投入物としての家畜糞尿、下水汚泥等もその組成変動があるので、適宜に高分子凝集剤の添加量を加減して用いる。
最終段階で用いるスクリュープレス機は、加圧が高いのが望ましく、通常は30kpa〜50kpaの範囲の加圧が行われる。このプレス機にて脱水ケーキと脱離液が分離排出するが、この脱離液は窒素分10〜20%、燐酸成分3〜10%、カリウム成分5〜15%を含んでおり、農作物などの液肥として用いることも可能である。
本発明に使用する消石灰は、初期投入後の継続運転にてペーハー調整レベルが低下するので、適宜に追加投入を行う。通常はフィーダー等を用いて自動投入がなされる。
例えば、焼酎製造により発生する汚泥はペーハー3.5程度であり、脱離液とこの汚泥を50:50の比率で混合した場合にはペーハー値は5.1程度になり、消石灰の追加(重量比1パーセント未満)にてペーハー値7程度まで改善される。なお、汚泥に対する脱離液の混合比率にて追加消石灰の必要量は変化し、汚泥に対し3倍の脱離液混合(容積比)では0.14パーセント、逆に汚泥に対し33パーセントの脱離液混合では約1パーセントの追加消石灰が必要となる。本装置を用いずに単なる消石灰投入によるペーハー調整に比べ、本装置使用によるペーハー調整では使用する消石灰の量は約25パーセント程度となり、大幅なトータルコストの低減となる。エアレーションタンクでは脱離液をエアレーションするが、このエアレーションは連続的になされ、投入された脱離液は連続的に混入タンクへ移送されるが、投入された脱離液が受ける平均的なエアレーション時間は30分以上である。なお、混入タンクに投入される脱離液と汚泥の比が適正に保たれるよう、脱離液送水ポンプと汚泥移送ポンプの移送能力を適宜に選択することが望ましく、同様に混合液移送ポンプや脱離液移送ポンプについても同様である。
By the means described above, a product separated into a dehydrated liquid and a treated product can be obtained, but this desorbed liquid has significantly reduced BOD (biological oxygen demand) and suspended sludge compared to the input, and nitrogen. A decrease in content and phosphorus content is also observed. In addition, the dehydrated product has a structure in which celluloses having different lengths are entangled vertically and horizontally, and has a feature of high moisture absorption and water absorption and high moisture release.
In the means of the present invention, the order of addition of the wood fiber and the polymer flocculant is important. First, the wood fiber is added to the input material and stirred to form a slurry, and then the polymer flocculant is added and stirred. If this order is reversed, floc (a mixture of water and sludge) is not formed, and the expected dehydration effect cannot be obtained.
The wood fiber used in the present invention is one that has been subjected to sun drying or the like so that the water content is about 15%. When the fiber content of the input is high, the amount of addition is reduced, and when it is low It may be used by adjusting according to the situation such as increasing, and other fiber materials such as disposable chopsticks, old wood chips and straw may be used for wood fiber. Moreover, since livestock manure, sewage sludge, etc. as input materials also vary in composition, the amount of polymer flocculant added is appropriately adjusted.
The screw press used in the final stage desirably has high pressurization, and usually pressurization in the range of 30 kpa to 50 kpa is performed. This press machine separates and discharges the dehydrated cake and the detachment liquid. This detachment liquid contains 10 to 20% nitrogen, 3 to 10% phosphoric acid component, and 5 to 15% potassium component. It can also be used as liquid fertilizer.
Since the pH adjustment level of the slaked lime used in the present invention is lowered in the continuous operation after the initial charging, additional charging is appropriately performed. Usually, automatic feeding is performed using a feeder or the like.
For example, sludge generated by shochu production has a pH of about 3.5, and when the desorbed liquid and this sludge are mixed at a ratio of 50:50, the pH value becomes about 5.1 and additional slaked lime (weight) It is improved to a pH value of about 7 at a ratio of less than 1 percent). The required amount of additional slaked lime varies depending on the mixing ratio of the desorbed liquid with respect to the sludge. About 1 percent additional slaked lime is required for the weaning mixing. Compared to the pH adjustment by simply using slaked lime without using this device, the amount of slaked lime used in the pH adjustment by using this device is about 25%, which greatly reduces the total cost. The aeration tank aerates the desorbed liquid, but this aeration is performed continuously, and the introduced desorbed liquid is continuously transferred to the mixing tank, but the average aeration time received by the introduced desorbed liquid Is 30 minutes or more. In addition, it is desirable to appropriately select the transfer capacity of the desorption liquid feed pump and the sludge transfer pump so that the ratio of the desorption liquid and the sludge charged into the mixing tank is maintained appropriately. Similarly, the mixed liquid transfer pump This also applies to the desorption liquid transfer pump.

以上、本発明について説明したが、本発明は消石灰を用いるとともに脱離液再利用にてペーハー値の調整を行い、吸水性の高い木質繊維と安全性の高い無機質高分子凝集剤の双方を用いるところにその特徴を有し、短期間でのコンポスト化を可能とするコンポスト原料を製造する手段を提供するものである。
従来は多種多様な有機または無機の高分子凝集剤あるいはこれらを組み合わせて用いているが、凝集剤の中には重金属と同様の成分を有するものや、アクリルアミド系物質が含まれたものがあり、このような凝集剤を用いた場合にはコンポスト化して使用するときに土壌や作物の安全性が確保されない問題があったが、本発明によってより安全性の高いコンポスト化が可能となったのである。
なお、実施形態においては、流量調整槽およびフロック槽を設けたので、凝集槽およびスクリュープレス機への処理物の急激な流入を防止して円滑なる処理が得られる。
また、貯留槽内にカッター付き水中汚物ポンプを用いたので、混合槽へ移送する前に投入物の固形成分を完全に破砕して移送することができる。
本発明に用いる木質繊維およびカチオン性天然高分子凝集剤は、情報収集と研究を重ねた結果見出されたもので、吸湿性が高く発酵速度の速い木質繊維と、食品応用が可能な高分子凝集剤を発見したものであり、これらを順序よく用いることにより、投入物粘度を次第に高めるとともにフロック形成がなされ、従来手段に比べ約30%程度に減容された脱水ケーキが得られ、所望の処理物が得られるのである。
以上のごとく、本発明によって適正ペーハー値と適正含水率を有したコンポスト化用原料の製造方法とその装置を得ることができる。
Although the present invention has been described above, the present invention uses slaked lime and adjusts the pH value by reusing the detachment liquid, and uses both highly water-absorbing wood fibers and highly safe inorganic polymer flocculants. However, the present invention provides a means for producing a compost raw material having the characteristics and enabling composting in a short period of time.
Conventionally, a wide variety of organic or inorganic polymer flocculants or combinations thereof are used, but some flocculants have the same components as heavy metals and some contain acrylamide substances. When such a flocculant was used, there was a problem that the safety of soil and crops was not ensured when used after composting, but the present invention enabled composting with higher safety. .
In the embodiment, since the flow rate adjustment tank and the flock tank are provided, a smooth process can be obtained by preventing a rapid inflow of the processed material into the aggregation tank and the screw press machine.
Moreover, since the underwater waste pump with a cutter was used in the storage tank, the solid component of the input can be completely crushed and transferred before being transferred to the mixing tank.
The wood fiber and cationic natural polymer flocculant used in the present invention were found as a result of repeated information gathering and research. The wood fiber having high hygroscopicity and high fermentation rate, and the polymer capable of food application. The flocculant has been discovered, and by using these in order, the viscosity of the feed is gradually increased and flocs are formed, resulting in a dehydrated cake whose volume is reduced to about 30% compared to the conventional means, and the desired treatment. Things are obtained.
As described above, according to the present invention, a method for producing a composting raw material having an appropriate pH value and an appropriate water content and an apparatus therefor can be obtained.

本発明装置の構造説明図  Structure explanatory diagram of the device of the present invention

符号の説明Explanation of symbols

1 エアレーションタンク
2 エアーコンプレッサー
3 送気管
4 汚泥貯留タンク
5 混入タンク
6 脱離液移送管
7 脱離液送水ポンプ
8 汚泥移送管
9 汚泥移送ポンプ
10 混合液移送管
11 混合液移送ポンプ
12 脱離液投入管
13 脱離液移送ポンプ
14 汚泥投入管
21 貯留槽
22 カッター付き水中汚物ポンプ
23 攪拌機
24 回転軸
25 羽根
26 液面制御電極棒
27 混合槽
28 水中汚物ポンプ
29 攪拌機
30 液面制御電極棒
31 流量調整槽
32 邪魔板
33 凝集槽
34 攪拌機
35 液面制御電極棒
36 薬剤タンク
37 薬注ポンプ
38 添加剤タンク
39 ブロワー
40 フロック槽
41 スクリュープレス機
42 脱水ケーキ排出口
43 脱離液排出口
44 ドレンバルブ
45 ドレンバルブ
46 ドレンバルブ
50 攪拌物移送管
51 流量調整弁
52 オーバーフロー管
53 添加剤移送管
54 流量調整弁
55 一次混合移送管
56 オーバーフロー管
57 薬注管
58 二次混合移送管
DESCRIPTION OF SYMBOLS 1 Aeration tank 2 Air compressor 3 Air supply pipe 4 Sludge storage tank 5 Mixing tank 6 Desorption liquid transfer pipe 7 Desorption liquid water pump 8 Sludge transfer pipe 9 Sludge transfer pump 10 Mixture transfer pipe 11 Mixture transfer pump 12 Desorption liquid Input pipe 13 Desorption liquid transfer pump 14 Sludge input pipe 21 Storage tank 22 Underwater filth pump with cutter 23 Stirrer 24 Rotating shaft 25 Blade 26 Liquid level control electrode rod 27 Mixing tank 28 Underwater filth pump 29 Stirrer 30 Liquid level control electrode bar 31 Flow control tank 32 Baffle plate 33 Coagulation tank 34 Stirrer 35 Liquid level control electrode rod 36 Drug tank 37 Chemical injection pump 38 Additive tank 39 Blower 40 Flock tank 41 Screw press machine 42 Dehydrated cake discharge port 43 Desorbed liquid discharge port 44 Drain Valve 45 Drain valve 46 Drain valve 50 Stirring Object transfer pipe 51 flow regulating valve 52 overflow pipe 53 additives transfer line 54 flow regulating valve 55 primary mixing transfer pipe 56 overflow pipe 57 Kusurichukan 58 secondary mixing transfer tube

Claims (2)

1.脱離液をエアレーションする第一工程。
2.エアレーション後の脱離液にコンポスト化対象物を混入する第二工程。
3.混入後の液に必要に応じて適宜に消石灰を投入する第三工程。
4.第三工程で得られた液に木質繊維を加えて攪拌する第四工程。
5.木質繊維添加攪拌後の物質に高分子凝集剤を加えて攪拌する第五工程。
6.高分子凝集剤添加攪拌後の物質を圧搾・脱水する第六工程。
7.第六工程で得られた脱離液を第一工程に戻してエアレーションする第七工程。
以上の各工程からなることを特徴とするコンポスト化用原料の製造方法。
1. The first step of aerating the desorbed liquid.
2. A second step in which the composting target is mixed into the desorbed liquid after aeration.
3. A third step in which slaked lime is appropriately added to the mixed liquid as necessary.
4). A fourth step of adding wood fiber to the liquid obtained in the third step and stirring.
5). The fifth step of adding and stirring the polymer flocculant to the substance after the addition of the wood fiber.
6). Sixth step of squeezing and dewatering the material after adding and stirring the polymer flocculant.
7). A seventh step of returning the desorbed liquid obtained in the sixth step to the first step and aeration.
A method for producing a composting raw material comprising the steps described above.
エアレーション機能を備えたエアレーションタンクと、汚泥貯留タンクと、混入タンクを各々設け、エアレーションタンクと汚泥貯留タンクの貯留物を混入タンクへ投入する手段を設け、一方、適宜形状・サイズの中空体による貯留槽、混合槽、凝集槽、添加剤タンク、薬剤タンクを各々設け、貯留槽内下部にカッター付き水中汚物ポンプ、混合槽内下部に水中汚物ポンプを各々設置し、貯留槽と混合槽および凝集槽に、羽根を有し槽の上方から下方に向かう回転軸を回転させるモーターを有する攪拌機を各々設け、薬剤タンクに薬注ポンプ、添加剤タンクにブロワーを各々設け、前記カッター付き水中汚物ポンプの吐出口と混合槽の上部、水中汚物ポンプの吐出口と凝集槽上部を各々配管接続するとともに、ブロワー吐出口と混合槽上部、薬注ポンプ吐出口と凝集槽上部を各々配管接続し、一方、スクリュープレス機を設けるとともに該スクリュープレス機の入り口と凝集槽下部を配管接続し、前記の混入タンク底部と貯留槽上部を配管接続し、スクリュープレス機の脱離液排出口とエアレーションタンクを配管接続し、必要に応じ各配管途中にポンプを位置させ、各電動機器への通電制御システムを設けることにより、投入されたコンポスト化対象物のペーハー調整を行い、攪拌し、木質繊維を加えて攪拌し、さらに高分子凝集剤を加えて攪拌後、圧搾・脱水してコンポスト化用原料を製造するとともに、この脱水して得られる脱離液を再びエアレーションして再利用することにより、低コストでのペーハー調整と適正保水率のコンポスト化用原料が得られるよう構成したことを特徴とするコンポスト化用原料の製造装置。  An aeration tank with an aeration function, a sludge storage tank, and a mixing tank are provided, and a means for introducing the aeration tank and sludge storage tank into the mixing tank is provided. A tank, a mixing tank, a coagulation tank, an additive tank, and a chemical tank are provided, an underwater waste pump with a cutter is installed in the lower part of the storage tank, and an underwater waste pump is installed in the lower part of the mixing tank. In addition, a stirrer having a blade and a motor for rotating a rotating shaft from the upper side to the lower side of the tank is provided, a chemical injection pump is provided in the drug tank, and a blower is provided in the additive tank, respectively. While connecting the outlet and the upper part of the mixing tank, the discharge port of the submersible waste pump and the upper part of the coagulation tank, respectively, the blower discharge port and the upper part of the mixing tank, Note: The pump discharge port and the upper part of the coagulation tank are connected by piping, while a screw press machine is provided, the inlet of the screw press machine and the lower part of the coagulation tank are connected by piping, and the bottom of the mixing tank and the upper part of the storage tank are connected by piping The connected composting object is established by connecting the release port of the screw press machine and the aeration tank by piping, positioning the pump in the middle of each piping as necessary, and providing a power supply control system for each electric device. After adjusting the pH of the mixture, stirring, adding the wood fiber, stirring, further adding the polymer flocculant, stirring, pressing and dewatering to produce a composting raw material, the desorption obtained by this dehydration It was constructed so that raw materials for composting with pH adjustment and proper water retention ratio can be obtained at low cost by re-aeration and reuse of the liquid Raw material manufacturing apparatus for composting characterized.
JP2006142044A 2006-04-19 2006-04-19 Method and apparatus for producing compost raw material Pending JP2007284332A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010137158A (en) * 2008-12-11 2010-06-24 Kubota Kankyo Service Kk Apparatus for measuring fiber concentration in sludge, apparatus for adjusting fiber concentration in sludge, dehydration equipment and dehydration method
CN102633421A (en) * 2012-04-18 2012-08-15 湖南大学 Sludge drying method
CN104176899A (en) * 2014-09-03 2014-12-03 长兴日月环保机械有限公司 Sludge treatment device and method

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010137158A (en) * 2008-12-11 2010-06-24 Kubota Kankyo Service Kk Apparatus for measuring fiber concentration in sludge, apparatus for adjusting fiber concentration in sludge, dehydration equipment and dehydration method
CN102633421A (en) * 2012-04-18 2012-08-15 湖南大学 Sludge drying method
CN102633421B (en) * 2012-04-18 2013-08-07 湖南大学 Sludge drying method
CN104176899A (en) * 2014-09-03 2014-12-03 长兴日月环保机械有限公司 Sludge treatment device and method

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