JP2539728B2 - Method and apparatus for promoting fermentation of organic sludge using an inclined surface - Google Patents
Method and apparatus for promoting fermentation of organic sludge using an inclined surfaceInfo
- Publication number
- JP2539728B2 JP2539728B2 JP4300645A JP30064592A JP2539728B2 JP 2539728 B2 JP2539728 B2 JP 2539728B2 JP 4300645 A JP4300645 A JP 4300645A JP 30064592 A JP30064592 A JP 30064592A JP 2539728 B2 JP2539728 B2 JP 2539728B2
- Authority
- JP
- Japan
- Prior art keywords
- fermentation
- inclined surface
- primary
- water content
- mixture
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
- 238000000855 fermentation Methods 0.000 title claims description 98
- 230000004151 fermentation Effects 0.000 title claims description 98
- 238000000034 method Methods 0.000 title claims description 16
- 239000010802 sludge Substances 0.000 title claims description 14
- 230000001737 promoting effect Effects 0.000 title claims description 10
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 29
- 239000000203 mixture Substances 0.000 claims description 23
- 239000000463 material Substances 0.000 claims description 15
- 239000010801 sewage sludge Substances 0.000 claims description 14
- 238000000151 deposition Methods 0.000 claims description 12
- 230000008021 deposition Effects 0.000 claims description 11
- 239000002893 slag Substances 0.000 claims description 6
- 238000004062 sedimentation Methods 0.000 claims description 4
- 230000000717 retained effect Effects 0.000 claims description 3
- 230000003247 decreasing effect Effects 0.000 claims 1
- 239000000047 product Substances 0.000 description 32
- 230000035699 permeability Effects 0.000 description 6
- 238000002485 combustion reaction Methods 0.000 description 5
- 238000002156 mixing Methods 0.000 description 5
- 230000035515 penetration Effects 0.000 description 5
- 238000003756 stirring Methods 0.000 description 4
- 238000005273 aeration Methods 0.000 description 3
- 239000003610 charcoal Substances 0.000 description 3
- 238000007796 conventional method Methods 0.000 description 3
- 238000004332 deodorization Methods 0.000 description 3
- 238000003860 storage Methods 0.000 description 3
- 239000002361 compost Substances 0.000 description 2
- 238000007599 discharging Methods 0.000 description 2
- 239000000835 fiber Substances 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 238000012856 packing Methods 0.000 description 2
- 239000012466 permeate Substances 0.000 description 2
- 239000000843 powder Substances 0.000 description 2
- 239000004576 sand Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000012546 transfer Methods 0.000 description 2
- 229920002752 Konjac Polymers 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 239000000853 adhesive Substances 0.000 description 1
- 230000001070 adhesive effect Effects 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 238000003763 carbonization Methods 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 238000004891 communication Methods 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000005520 cutting process Methods 0.000 description 1
- 230000006378 damage Effects 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000001877 deodorizing effect Effects 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 238000007689 inspection Methods 0.000 description 1
- 239000011810 insulating material Substances 0.000 description 1
- 238000009413 insulation Methods 0.000 description 1
- 235000010485 konjac Nutrition 0.000 description 1
- 239000010871 livestock manure Substances 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 230000009965 odorless effect Effects 0.000 description 1
- 230000002093 peripheral effect Effects 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
Landscapes
- Treatment Of Sludge (AREA)
- Fertilizers (AREA)
Description
【発明の詳細な説明】Detailed Description of the Invention
【0001】[0001]
【産業上の利用分野】本発明は傾斜面を利用した有機汚
泥物の醗酵促進方法及び醗酵促進装置に関するもので、
醗酵機械で醗酵処理しても、なお且つ水分調整が不完全
で未熟成の醗酵物に自然なエア−レイション(醗酵物に
空気を触れさすための混ぜ返し又は切り返し)を繰り返
して行えるようにすることによって醗酵効率をより高め
るようにし、且つ一次醗酵物を所定容量づつ通気性の良
い袋体に詰めて一定の期間を経過させることにより、よ
り一層熟成した二次醗酵物が得られるようにしたことを
目的とする。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and apparatus for promoting fermentation of organic sludge using an inclined surface,
Even if the fermentation process is carried out by a fermentation machine, it is possible to repeatedly perform natural air-ration (mixing or cutting back to expose the fermentation product to the air) to the fermentation product that is incomplete in moisture adjustment and immature. By further increasing the fermentation efficiency by, and by packing the primary fermentation product in a bag with good air permeability in a predetermined volume for a certain period of time, a further fermented secondary fermentation product was obtained. The purpose is to
【0002】[0002]
【従来の技術】本願出願人は、先にPMC工法と呼ぶリ
サイクル緑化工法を提供した(特公平4−45613号
公報及び特開平4−261914号公報参照)。そのP
MC工法とは、公共下水汚泥や家畜糞のコンポストと木
炭粉、又は当該コンポストとパルプ製造時に生じるパル
プ滓の焼却灰等各種産業から発生する焼却灰を混合した
後醗酵させて有機質系の生育基盤材を生産し、この生育
基盤材と、コンニャク飛粉を主原料とした「ピ−エムザ
イ(登録商標)」と称する粘着材を使用して、緑化工事
における植物の生育基盤の形成を行う工法である。2. Description of the Related Art The applicant of the present application previously provided a recycling greening method called a PMC method (see Japanese Patent Publication No. 4-45613 and Japanese Patent Application Laid-Open No. 4-261914). That P
The MC method is an organic growth base that is produced by mixing compost of public sewage sludge or livestock manure and charcoal powder, or incineration ash generated from various industries such as incineration ash of pulp slag produced during pulp manufacturing and fermentation. A method of producing a growth base of plants in a revegetation work by producing a wood and using this growth base material and an adhesive material called "P-MZAI (registered trademark)" which mainly uses konjak flying powder. is there.
【0003】[0003]
【発明が解決しようとする課題】上記のPMC工法によ
って、従来工法で植生基盤材として用いる黒土や山砂等
の代用となるほか、肥料分も多く含まれている。さら
に、山砂採取による自然破壊の防止と、廃棄物のリサイ
クルできる現代的な工法として有益である。他方、前記
のPMC工法において、有機物の醗酵促進には、水分調
整の出来不出来が醗酵完了の期間を左右する。本願出願
人の前記従来工法では、キルン型(横型)醗酵機械の使
用によって、有機汚泥物の水分調整が不良である場合、
醗酵機械より吐出された水分の多い不良な未熟成の堆肥
は、再度水分調整を行う必要がある。ところが、従来工
法においては未熟成醗酵物の再度の水分調整を行うの
に、再度醗酵機械に投入して醗酵させるか、又は長期間
堆積しておき、その未熟成醗酵物を人手又は機具を介し
てエア−レイションを繰り返し行う以外には、より有効
且つ適切な方法が見出せなかった。The above-mentioned PMC method substitutes black soil and mountain sand used as a vegetation base material in the conventional method, and also contains a large amount of fertilizer. Furthermore, it is useful as a modern construction method that prevents the destruction of nature by collecting sand and recycles waste. On the other hand, in the above-mentioned PMC method, in order to promote the fermentation of organic substances, the failure of adjusting the water content affects the period of completion of the fermentation. In the conventional method of the applicant of the present application, when the water content of the organic sludge is poorly adjusted by using a kiln type (horizontal type) fermentation machine,
Poor and unripe compost with a large amount of water discharged from the fermentation machine needs to be adjusted again. However, in the conventional method, in order to adjust the water content of the unripened fermented material again, it is put into the fermenting machine again for fermentation, or it is accumulated for a long time, and the unripened fermented material is manually or through a device. No more effective and appropriate method could be found other than repeating the aeration.
【0004】[0004]
【課題を解決するための手段】そこで、本発明は従来公
報の課題を解決し、且つ発明の目的を達成するために提
供するものである。すなわち、本発明の第1は、傾斜面
を利用した有機汚泥物の醗酵促進方法において、下水汚
泥にパルプ滓の焼却灰を略均等の割合で混合して適度に
脱臭と水分調整した混合物を醗酵機械に投入し、醗酵機
械の胴部の回転によって、混合物を撹拌しながら移送す
ると共に、バーナーによる加熱空気を混合物の表面に接
触するように供給し、醗酵機械の吐出口から吐出した一
次醗酵物を下方の傾斜面に連続的に落下させ、当該傾斜
面において水分調整が良好な一次醗酵物を滑落して下端
の堆積位置に堆積し、水分が多くて調整不良の一次醗酵
物は傾斜面の角度に対する水分を含む自重で前記傾斜面
に一時滞留し、当該滞留位置で外気を浸透接触させて醗
酵を活発化し、時間の経過によって水分が減少した前記
傾斜面に滞留した一次醗酵物を傾斜面下端の堆積位置に
滑落落下するようにしたものである。Therefore, the present invention is provided to solve the problems of the prior art publications and to achieve the object of the invention. That is, a first aspect of the present invention is a method for promoting fermentation of an organic sludge using an inclined surface, wherein a mixture of incinerated ash of pulp slag is mixed with sewage sludge in a substantially equal ratio to appropriately deodorize and ferment the mixture. The primary fermented substance discharged from the discharge port of the fermentation machine was charged into the machine and the mixture was transferred with stirring by rotating the body of the fermentation machine and heated air by the burner was supplied so as to contact the surface of the mixture. Is continuously dropped to the lower inclined surface, the primary fermentation product with good water content is slid down on the inclined surface and deposited at the lower end deposition position, and the primary fermentation product with a large amount of water that is poorly adjusted is on the inclined surface. and temporarily stay on the inclined surface by its own weight, including moisture for the angle, intensified fermentation by the outside air infiltrated contacted in the dwell position, the inclined surface of the primary fermentation product that accumulated on the inclined surface moisture is reduced by the passage of time It is obtained so as to slide down fall deposition position of the edge.
【0005】本発明の第2は傾斜面を利用した有機汚泥
物の醗酵促進装置において、一端に混合物の投入口を有
し、他端に吐出口を有するキルン型醗酵機械において、
その醗酵機械の吐出口の下方に、醗酵処理されて吐出し
た水分調整が良好な一次醗酵物が落下すると傾斜面下端
まで滑落し、且つ水分調整が不良で未熟成な醗酵物が落
下すると水分を含む自重で一時滞留する30度〜60度
の角度を可とする傾斜面を形成し、且つその傾斜面の下
端位置に水分調整が良好な一次醗酵物を滑落落下して堆
積しておく堆積場を形成したものである。A second aspect of the present invention is an apparatus for promoting fermentation of organic sludge using an inclined surface, which is a kiln type fermentation machine having a mixture inlet at one end and an outlet at the other end,
Below the discharge port of the fermentation machine, when the fermented product that has been fermented and discharged with good water content adjustment falls, it will slide to the lower end of the inclined surface, and if the immature fermented material with poor water content adjustment falls, the water content will drop. Including 30 to 60 degrees that temporarily stays under its own weight
The angle forming a sloping surface to variable is and what is water adjusted to a lower end position of the inclined surface to form a deposition field to be deposited slides down falling good primary fermentation product.
【0006】本発明の第3は第1の発明に係る傾斜面を
利用した有機汚泥物の醗酵促進方法において、堆積場に
落下到達した一次醗酵物を、外気が通過する程度の大容
量に設定して袋体に袋詰めして所定の期間貯蔵して二次
醗酵をさせたものである。A third aspect of the present invention is a method for promoting fermentation of an organic sludge using an inclined surface according to the first aspect of the invention, wherein the primary fermented material that has reached the sedimentation site is set to have a large capacity for the outside air to pass through. Then, it is packaged in a bag, stored for a predetermined period of time, and then subjected to secondary fermentation.
【0007】[0007]
【作用】汚泥運搬車から下水汚泥を所定の混合処理場に
降ろし、次いで、木炭繊維を炭化した40〜60°C程
度の熱を有するバルプ滓の焼却灰を当該下水汚泥と50%
づつの割合で加えて混合する。これによってパルプ滓の
燃焼灰は熱交換作用で温度が下がるが、汚泥の水分を調
整して醗酵を促し、且つ前記下水汚泥から発生する悪臭
は当該燃焼灰との混合でかなりの脱臭作用が生じる。次
にキルン型醗酵機械の一端の投入口から前記の水分調整
と脱臭化がなされた混合物を投入し、当該醗酵機械内に
バ−ナ−によって加熱空気を供給して混合物の表面に接
触させ、醗酵機械の胴部の回転によって、混合物の撹拌
と移送を行って醗酵作用と脱臭作用行いながら吐出口か
ら一次醗酵物を吐出して傾斜面に落下させる。この傾斜
面において、水分調整が良好な一次醗酵物は滑落して傾
斜面下端の堆積場に堆積される。そして、水分調整が不
良で未熟成の一次醗酵物は傾斜面に一時滞留するが、そ
の滞留個所においてもかなりの熱が保持され、且つ外気
の浸透によって醗酵し続けられ、水分調整が良好の状態
になると、滑落が始まって傾斜面下端の堆積場まで滑落
する。そして、これを通気性の良い袋体に外気が浸透す
る程度の大容量に設定して袋詰めして1〜3ケ月保管し
ておくことにより、自然的に二次醗酵が始まり、完全に
熟成した二次醗酵物が得られ、殆ど無臭化した黒っぽい
土状の生育基盤材が生産される。[Operation] The sewage sludge is unloaded from the sludge carrier to the prescribed mixing treatment plant, and then the incineration ash of the valp slag having carbonized charcoal fiber and having a heat of about 40 to 60 ° C. and 50% of the sewage sludge
Add and mix at a rate of one at a time. As a result, the temperature of the combustion ash of pulp slag decreases due to the heat exchange action, but the moisture of the sludge is adjusted to promote fermentation, and the malodor generated from the sewage sludge causes a considerable deodorizing action when mixed with the combustion ash. . Next, the mixture having the water content adjusted and deodorized is charged from the charging port at one end of the kiln type fermentation machine, and heated air is supplied to the surface of the mixture by a burner in the fermentation machine, By rotating the body of the fermentation machine, the mixture is stirred and transferred to perform fermentation and deodorization, and the primary fermentation product is discharged from the discharge port and dropped onto the inclined surface. On this slope, the primary fermented product with a good water content slides down and is deposited on the bottom of the slope. And, the primary fermentation product which is not matured due to poor moisture control is temporarily retained on the inclined surface, but considerable heat is retained even at the retention point, and the fermentation is continued by permeation of the outside air, and the moisture regulation is in a good state. Then, it starts to slide down and slides down to the deposit area at the bottom of the slope. Then, by setting this to a large volume that allows the outside air to permeate the bag with good air permeability, bag it, and store it for 1 to 3 months, the secondary fermentation will naturally start and it will mature completely. The secondary fermented product is obtained, and an almost odorless, dark soil-like growth base material is produced.
【0008】[0008]
【実施例】次に本発明の実施例を図面を以て説明する。
図1は本発明に係る傾斜面を利用した有機汚泥の醗酵促
進工程を示す概略側面図、図2は下水汚泥の醗酵促進方
法を実施する醗酵機械の正面図、図3は図2の平面図、
図4は図2の4−4線に沿う断面図である。図におい
て、1は醗酵機械の回転ドラム、2は下水汚泥11 とパ
ルプ滓の燃焼灰12 から成る混合物Mの投入チャンバ
−、3は一次醗酵物の吐出チャンバ−、4は加熱空気の
貫通チャンバ−であり、これらを主要素としてキルン型
醗酵機械Aが構成されている。前記の醗酵機械Aは基礎
台面Bに据付けられ、回転ドラム1が混合物の投入チャ
ンバ−2と吐出チャンバ−3で連結支持されている。ま
たこの回転ドラム1は基礎台面Bに設置した左右一対の
ロ−ラ−5によって回転自在に支持されている。そし
て、回転ドラム1内の軸線方向において、混合物の投入
チャンバ−2と吐出チャンバ−3とで、熱風貫通チャン
バ−4を固定支持している。また、前記の回転ドラム1
はその外周に駆動チェ−ン9が設けられ、その駆動チェ
−ン9にモ−タ−7により駆動されるスプロケット6を
噛合している。11は回転ドラム1の内周面に設けた複
数の送り羽根であり、互いに軸線に対して反対方向に螺
旋状に突設し、その送り羽根は吐出チャンバ−3側へ送
るように傾斜している。また回転ドラム1の外周は断熱
材8が被覆されている。12は回転ドラム1における熱
風貫通チャンバ−4に連通して設けたア−ム形の吸排気
管であり、その先端の出入口121 が吐出口22の方向
に向けて設置されている。13は前記の吸排気管12と
同じように熱風貫通チャンバ−4に設けた攪拌ア−ムを
示すが、ア−ム自体は無垢であり、当該チャンバ−とは
連通していない。投入チャンバ−2にはホッパ−10が
備えられていて、混合物はここからドラム内に投入され
る。投入チャンバ−2内の熱風貫通チャンバ−4の端部
にはダクト14が接続され、且つその途中にはダンパ−
15が設けられている。吐出チャンバ−3には、バ−ナ
−18及び温度センサ−19が設けられ、且つ必要に応
じて回転ドラム1に常に新鮮な熱風を送るために送風フ
ァン21が取付けられる。なお、前記吐出チャンバ−に
はドラム内で醗酵を始めている混合物Mを攪拌しながら
移送する一次醗酵物M′を吐出するための吐出口22が
設けられている。24は醗酵機械の吐出口22の下方に
形成した下り勾配の傾斜面であり、具体的には、勾配角
度θが30〜60度、横幅は約5m、長さは15m程度
に設定する。そして、前記吐出口と傾斜面が離れている
ときは、ベルトコンベヤを配置して一次醗酵物を搬送す
る。25は傾斜面の下端部位に形成した一次醗酵物M′
の堆積場、26はその一次醗酵物をさらに醗酵させるた
めの二次醗酵用堆積場であり、当該堆積場は必要に応じ
て設置するものとする。27はベルトコンベヤ、28は
傾斜面24から堆積場 に落下した一次醗酵物M′を袋
詰めする通気性の良い袋体であり、その袋体の容積は、
醗酵物内部への外気を浸透できる程度の大容量とするた
めに一袋当たり1立方mに設定する。なお、一次醗酵物
M′を必要に応じて傾斜面下端の堆積場に一時堆積して
おき、二次醗酵を開始してから袋体28に詰めることも
ある。29は袋詰めした袋体28を簀の子又は木製格子
30を介して多段積みする貯蔵場である。Embodiments of the present invention will now be described with reference to the drawings.
1 is a schematic side view showing a fermentation promoting process of organic sludge using an inclined surface according to the present invention, FIG. 2 is a front view of a fermentation machine for carrying out a fermentation promoting method of sewage sludge, and FIG. 3 is a plan view of FIG. ,
FIG. 4 is a sectional view taken along line 4-4 of FIG. In the figure, reference numeral 1 denotes a rotary drum fermentation machine 2 mixture M introduced chamber consisting of ash 1 2 sewage sludge 1 1 and pulp debris -, 3 the discharge chamber of the primary fermentation product -, 4 through the heated air It is a chamber, and a kiln-type fermentation machine A is constructed by using these as main elements. The fermentation machine A is installed on a base surface B, and the rotary drum 1 is connected and supported by a mixture input chamber-2 and a discharge chamber-3. The rotary drum 1 is rotatably supported by a pair of left and right rollers 5 installed on the base surface B. The hot-air penetration chamber 4 is fixedly supported by the mixture input chamber-2 and the discharge chamber-3 in the axial direction of the rotary drum 1. In addition, the rotary drum 1 described above
Is provided with a drive chain 9 on its outer periphery, and a sprocket 6 driven by a motor 7 is meshed with the drive chain 9. Reference numeral 11 denotes a plurality of feed blades provided on the inner peripheral surface of the rotary drum 1. The feed blades 11 are spirally projecting in directions opposite to each other with respect to the axis, and the feed blades are inclined to feed to the discharge chamber-3 side. There is. The outer periphery of the rotary drum 1 is covered with a heat insulating material 8. Reference numeral 12 denotes an arm-shaped intake / exhaust pipe provided so as to communicate with the hot air penetration chamber 4 in the rotary drum 1, and the inlet / outlet 12 1 at the tip thereof is installed toward the outlet 22. Reference numeral 13 denotes a stirring arm provided in the hot air penetration chamber-4 like the intake / exhaust pipe 12, but the arm itself is pure and is not in communication with the chamber. The charging chamber-2 is equipped with a hopper-10 from which the mixture is charged into the drum. A duct 14 is connected to the end of the hot air penetration chamber-4 in the charging chamber-2, and a damper is provided in the middle thereof.
15 are provided. The discharge chamber-3 is provided with a burner 18 and a temperature sensor-19, and a blower fan 21 is attached as necessary to always send fresh hot air to the rotary drum 1. The discharge chamber is provided with a discharge port 22 for discharging the primary fermentation product M ′ which transfers the mixture M which is starting fermentation in the drum while stirring. Reference numeral 24 denotes a downwardly sloping inclined surface formed below the discharge port 22 of the fermentation machine. Specifically, the inclination angle θ is set to 30 to 60 degrees, the width is set to about 5 m, and the length is set to about 15 m. When the discharge port and the inclined surface are separated, a belt conveyor is arranged to convey the primary fermentation product. 25 is the primary fermentation product M'formed at the lower end of the inclined surface
And 26 is a secondary fermentation deposition site for further fermenting the primary fermentation product, and the deposition site is to be installed if necessary. Reference numeral 27 is a belt conveyor, and 28 is a bag having good air permeability for packing the primary fermentation product M ′ that has fallen from the inclined surface 24 to the deposition site.
In order to have a large volume that allows the outside air to permeate inside the fermented product, it is set to 1 cubic meter per bag. In addition, the primary fermentation product M ′ may be temporarily accumulated in the accumulation field at the lower end of the inclined surface if necessary, and the secondary fermentation may be started before being packed in the bag 28. Reference numeral 29 is a storage space for stacking the packed bag bodies 28 in multiple stages via a cage or a wooden lattice 30.
【0009】[0009]
【具体的な工程例】下水汚泥処理場において、収集積載
して汚泥運搬車で運んできた悪臭を放つ下水汚泥11 を
所定の混合処理場Gに降ろし、ショベルカ−を介して木
炭繊維を炭化した40〜50°C程度のパルプ滓の燃焼
灰12 を当該下水汚泥と50%づつの割合で加えて混合
すると、燃焼灰12 は熱交換作用によって温度が下がる
が、下水汚泥11 の水分を調整して醗酵を促し、且つ前
記下水汚泥から発生する悪臭を燃焼灰12 の作用で相当
程度に脱臭が行われる。この場合、十分に混合された混
合物Mは、含水比が60%で、温度30°C程度になっ
ている。そして、パルプ滓の燃焼灰12 によって下水汚
泥から発生する悪臭が相当に脱臭される。次に、キルン
型醗酵機械Aの一端の投入ホッパ−10から前記の混合
物を投入し、当該醗酵機械内にバ−ナ−18による加熱
空気を回転ドラム1内に供給し、当該加熱空気を混合物
Mの表面に接触させ、且つ醗酵機械のドラム1の回転に
よって混合物Mの撹拌と移送を行って醗酵作用と脱臭作
用促進しながら吐出口22から堆肥化した一次醗酵物を
吐出する。吐出された一次醗酵物M′は、含水比が50
%で、且つ温度が50°C〜60°C程度を適正値とし
て設定する。吐出された一次醗酵物M′は下り勾配の傾
斜面24に落下し、その傾斜面において、含水比が適正
で水分調整が良好な一次醗酵物は、傾斜面を滑落して下
端の堆積場25に堆積される。そして、一次醗酵物のう
ち、水分が多くて含水比が50%を越える個所は、傾斜
面に落下したときにその傾斜面に滞留するが、その滞留
個所において一次醗酵物の滞留層内に外気の浸透により
醗酵が促進されて水分調整が良好な状態になると、再度
滑落が始まって堆積場25まで落下する。堆積場25に
堆積された一次醗酵物Mは、ショベルカ−S及びコンベ
ヤ27を使ってそのまま通気性を有する袋体28に詰め
た後、一定期間貯蔵しておくことによって袋体内で二次
醗酵し、人工的なエア−レイションを行わなくても醗酵
が促進され、より良く熟成した二次醗酵物M″となる。
なお、堆積場に堆積した一次醗酵物M′を他の二次醗酵
用堆積場26に移して1.5〜2.0m程度の高さに野
積みしておくこともあり、この場合は時間の経過によっ
て野積みした醗酵物の表面から50〜80cm程度の厚
さtまでは40〜60°C位の温度が上昇して二次醗酵
が始まって熟成する。そして、野積みしてある二次醗酵
物M″の熟成した部位をベルトコンベヤ27で搬送して
通気性の良い袋体28に充填する。充填した袋体28を
貯蔵場29に簀の子又は木製格子30を介して複数段に
積み重ねて貯蔵する。貯蔵中における袋体内の二次醗酵
物M″はエア−レイションをしないでも醗酵が促進され
る。なお、削られた二次醗酵物M″の野積みの山は、ま
たその表面から50〜80cmの厚さまで通気性が良く
なることによって、さらに二次醗酵が活発化する。11. Specific steps example sewage sludge treatment plant, collecting loading to unloading the sewage sludge 1 1 fetid that has carried in the sludge truck in a predetermined mixing treatment plants G, Shoberuka - charcoal fiber through carbonization If the was 40 to 50 ° C approximately pulp slag ash 1 2 adding and mixing at a rate of the sewage sludge and 50% increments, the combustion ash 1 2 the temperature is lowered by heat exchange action, sewage sludge 1 1 moisture encourage adjusted to fermentation, deodorization is effected malodors and generated from the sewage sludge in considerable under the action of combustion ash 1 2. In this case, the sufficiently mixed mixture M has a water content ratio of 60% and a temperature of about 30 ° C. The malodor generated from sewage sludge by combustion ash 1 2 pulp dregs are considerably deodorized. Next, the above mixture is charged from the charging hopper 10 at one end of the kiln type fermentation machine A, the heating air by the burner 18 is supplied into the rotary drum 1 in the fermentation machine, and the heating air is mixed. The composted primary fermentation product is discharged from the discharge port 22 while contacting the surface of M and rotating and rotating the drum 1 of the fermentation machine to agitate and transfer the mixture M to promote fermentation and deodorization. The discharged primary fermentation product M ′ has a water content ratio of 50.
%, And a temperature of about 50 ° C. to 60 ° C. is set as an appropriate value. The discharged primary fermented material M ′ drops onto the sloped surface 24 having a downward slope, and the primary fermented material having a proper water content ratio and good water content on the sloped surface slides down the sloped surface and is deposited at the lower end of the deposition field 25. Be deposited on. And, in the primary fermented product, a portion with a high water content and a water content ratio of more than 50% stays on the inclined surface when it falls on the inclined surface. Fermentation is promoted due to the permeation of water and the water content is adjusted to a good state, the sliding starts again and the water falls to the deposition site 25. The primary fermentation product M deposited on the deposition site 25 is packed in a breathable bag 28 as it is using the shoveler-S and the conveyor 27, and then stored for a certain period of time to carry out secondary fermentation in the bag. Fermentation is promoted without artificial aeration, resulting in a better-aged secondary fermentation product M ″.
The primary fermentation product M ′ deposited on the sedimentation site may be transferred to another secondary fermentation sedimentation site 26 and piled up in a height of about 1.5 to 2.0 m. As a result, the temperature of about 40 to 60 ° C rises from the surface of the fermented material piled up in the field to the thickness t of about 50 to 80 cm, and the secondary fermentation begins to ripen. Then, the aged portion of the secondary fermented matter M ″ which has been piled up is conveyed by the belt conveyor 27 to be filled in a bag 28 having good air permeability. The filled bag 28 is stored in the storage room 29 in a cage or a wooden lattice. It is stacked and stored in a plurality of stages via 30. During the storage, the secondary fermentation product M ″ in the bag body promotes fermentation without air-ration. The pile of piles of the scraped secondary fermentation product M ″ has a better air permeability up to a thickness of 50 to 80 cm from the surface thereof, so that the secondary fermentation is further activated.
【0010】[0010]
【発明の効果】本発明は上記の構成であるから、請求項
1及び請求項2においては、醗酵機械で醗酵処理して
も、なお且つ水分調整が不十分で未熟成の一次醗酵物を
所定角度の傾斜面に落下させることにより、その傾斜面
で自然なエア−レイションを人手を介さずに繰り返し行
え、これによって水分調整が十分となり、醗酵効率をよ
り高めることができ、品質が均一の生育基盤材を生産す
ることができる。また、請求項3にあっては、二次醗酵
を始めた醗酵物を通気性の良い袋体に袋詰めして所定の
期間貯蔵しておくことによって、人手を要するエア−レ
イションを節約することができる。しかも、そのエア−
レイションを省略したことにより、醗酵熱の分散が防止
することができる。また、袋詰めに用いる袋体は、直径
を1m以内とし、且つ一袋当たり1立方m程度の比較的
大容量の二次醗酵物を収容することにより、袋体内の中
心近くまで外気の浸透を図ることができ、醗酵がより一
層促進される。EFFECTS OF THE INVENTION Since the present invention has the above-mentioned constitution, in claims 1 and 2, even if the fermentation treatment is carried out by a fermentation machine, the water content is insufficient and the unripened primary fermentation product is specified. By dropping it on the inclined surface of the angle, it is possible to repeat the natural aeration on the inclined surface without human intervention, which makes it possible to adjust the water content sufficiently and increase the fermentation efficiency, and to ensure uniform quality growth. A base material can be produced. Further, according to claim 3, the fermented product having undergone the secondary fermentation is packed in a bag having good air permeability and stored for a predetermined period of time, thereby saving an air ratio which requires manpower. You can And that air
By omitting the ratio, dispersion of the fermentation heat can be prevented. In addition, the bag used for bagging has a diameter of 1 m or less and accommodates a relatively large volume of secondary fermented product of about 1 cubic m per bag, so that the outside air can penetrate to the vicinity of the center of the bag. The fermentation can be further promoted.
【図1】 本発明に係る傾斜面を利用した有機汚泥の醗
酵促進工程を示す概略側面図である。FIG. 1 is a schematic side view showing a process of promoting fermentation of organic sludge using an inclined surface according to the present invention.
【図2】 混合物の醗酵機械の正面図である。FIG. 2 is a front view of a fermentation machine for a mixture.
【図3】 図2の平面図である。FIG. 3 is a plan view of FIG.
【図4】 図2の4−4線に沿う断面図である。4 is a cross-sectional view taken along line 4-4 of FIG.
1 回転ドラム 2 投入チャンバ− 3 吐出チャンバ− 4 熱風貫通チャンバ− 5 回転ドラムの支持ロ−ラ− 6 スプロケット 7 減速機付きモ−タ− 8 断熱材 9 駆動チェ−ン 10 ホッパ− 11 送り羽根 12 ア−ム型吸排気管 13 攪拌ア−ム 14 投入チャンバ−側のダクト 15 ダクトのダンパ− 17 点検口 18 バ−ナ− 19 温度センサ− 20 ダンパ− 21 送風ファン 22 吐出口 24 下り勾配の傾斜面 25 一次醗酵物の堆積場 26 二次醗酵用堆積場 27 ベルトコンベヤ 28 袋体 1 Rotating Drum 2 Charge Chamber-3 Discharging Chamber-4 Hot Air Penetration Chamber-5 Rotating Drum Support Roller 6 Sprocket 7 Motor with Reducer 8 Insulation 9 Drive Chain 10 Hopper 11 Feeding Blade 12 Arm type intake / exhaust pipe 13 Stirring arm 14 Duct on the side of the charging chamber 15 Duct damper 17 Inspection port 18 Burner 19 Temperature sensor-20 Damper 21 Blower fan 22 Discharge port 24 Down slope 25 Primary fermentation deposits 26 Secondary fermentation deposits 27 Belt conveyor 28 Bags
Claims (3)
割合で混合して適度に脱臭と水分調整した混合物を醗酵
機械に投入し、醗酵機械の胴部の回転によって、混合物
を撹拌しながら移送すると共に、バーナーによる加熱空
気を混合物の表面に接触するように供給し、醗酵機械の
吐出口から吐出した一次醗酵物を下方の傾斜面に連続的
に落下させ、当該傾斜面において水分調整が良好な一次
醗酵物を滑落して下端の堆積位置に堆積し、水分が多く
て調整不良の一次醗酵物は傾斜面の角度に対する水 分を
含む自重で前記傾斜面に一時滞留し、当該滞留位置で外
気を浸透接触させて醗酵を活発化し、時間の経過によっ
て水分が減少した前記傾斜面に滞留した一次醗酵物を傾
斜面下端の堆積位置に滑落落下するようにしたことを特
徴とする傾斜面を利用した有機汚泥物の醗酵促進方法。1. A sewage sludge is mixed with incinerated ash of pulp slag at a substantially equal ratio, and the mixture is appropriately deodorized and the water content is adjusted, and the mixture is put into a fermentation machine. The mixture is agitated by rotating the body of the fermentation machine. While being transferred, the heated air from the burner is supplied so as to come into contact with the surface of the mixture, and the primary fermentation product discharged from the discharge port of the fermentation machine is continuously dropped onto the lower inclined surface, and the water content is adjusted on the inclined surface. by sliding down the good primary fermentation was deposited in the deposition position of the lower end, the primary fermentation of misalignment are much moisture the moisture with respect to the angle of the inclined surface
Temporarily stays on the inclined surface by its own weight, activates fermentation by permeating external air at the staying position, and the primary fermentation product retained on the inclined surface whose water content has decreased over time is accumulated at the lower end of the inclined surface. A method for accelerating the fermentation of organic sludge using an inclined surface, which is characterized in that it slid down onto the surface.
出口を有するキルン型醗酵機械において、その醗酵機械
の吐出口の下方に、醗酵処理されて吐出した水分調整が
良好な一次醗酵物が落下すると傾斜面下端まで滑落し、
且つ水分調整が不良で未熟成な醗酵物が落下すると水分
を含 む自重で一時滞留する30度〜60度の角度を可と
し、且つ長さが15 m程度に設定した傾斜面を形成し、
且つその傾斜面の下端位置に水分調整が良好な一次醗酵
物を滑落落下して堆積しておく堆積場を形成した傾斜面
を利用した有機汚泥物の醗酵促進装置。2. A kiln-type fermentation machine having a mixture inlet at one end and a discharge outlet at the other end, in the lower part of the outlet of the fermentation machine, the primary water content of the fermented product is adjusted and discharged. When the fermented material falls, it slides down to the bottom of the slope,
In addition, if the immature fermented product with poor water content control falls, the water content
A variable angle of 30-60 degrees to temporarily stay in including its own weight
And form an inclined surface with a length set to about 15 m ,
Also, an apparatus for promoting fermentation of organic sludge using an inclined surface, which forms a deposition site for sliding down and depositing a primary fermented material with good moisture adjustment at the lower end position of the inclined surface.
気が通過する程度の大容量に設定して袋体に袋詰めして
所定の期間貯蔵して二次醗酵をさせた傾斜面を利用した
有機汚泥物の醗酵促進方法。3. The primary fermented material that has reached the sedimentation site is set to a large volume that allows the outside air to pass through, is packed in a bag, and is stored for a predetermined period of time to allow the secondary fermentation to be performed. Method for promoting fermentation of organic sludge used.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4300645A JP2539728B2 (en) | 1992-10-14 | 1992-10-14 | Method and apparatus for promoting fermentation of organic sludge using an inclined surface |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4300645A JP2539728B2 (en) | 1992-10-14 | 1992-10-14 | Method and apparatus for promoting fermentation of organic sludge using an inclined surface |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH07275898A JPH07275898A (en) | 1995-10-24 |
JP2539728B2 true JP2539728B2 (en) | 1996-10-02 |
Family
ID=17887358
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JP4300645A Expired - Fee Related JP2539728B2 (en) | 1992-10-14 | 1992-10-14 | Method and apparatus for promoting fermentation of organic sludge using an inclined surface |
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KR100851947B1 (en) * | 2008-01-29 | 2008-08-12 | 보성환경산업(주) | Stabilization treatment device and method of sewage and water purification sludge |
JP5879006B1 (en) * | 2015-02-02 | 2016-03-08 | グリーンテックス株式会社 | Composting method using dehydrated cake |
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