JP2002177930A - Garbage treatment process - Google Patents

Garbage treatment process

Info

Publication number
JP2002177930A
JP2002177930A JP2000380865A JP2000380865A JP2002177930A JP 2002177930 A JP2002177930 A JP 2002177930A JP 2000380865 A JP2000380865 A JP 2000380865A JP 2000380865 A JP2000380865 A JP 2000380865A JP 2002177930 A JP2002177930 A JP 2002177930A
Authority
JP
Japan
Prior art keywords
garbage
core material
activated carbon
decomposition
treatment
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
Application number
JP2000380865A
Other languages
Japanese (ja)
Inventor
Shigehiko Harada
茂彦 原田
Akihito Otaki
昭仁 大滝
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Toho Chemical Engineering and Construction Co Ltd
Original Assignee
Toho Chemical Engineering and Construction Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Toho Chemical Engineering and Construction Co Ltd filed Critical Toho Chemical Engineering and Construction Co Ltd
Priority to JP2000380865A priority Critical patent/JP2002177930A/en
Publication of JP2002177930A publication Critical patent/JP2002177930A/en
Pending legal-status Critical Current

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  • Mixers Of The Rotary Stirring Type (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide an extinction type garbage treatment process which involves decomposition of garbage into a liquid and/or a gas by using a core material in an treatment vessel provided with a water spray port, agitation blades and a perforated plate and by which the activity of decomposition of the garbage into a liquid and/or a gas can be enhanced and also the COD of wastewater yielded by the garbage decomposition can be controlled at a low level without increasing the amount of water supply to the garbage. SOLUTION: Garbage is subjected to biological decomposition into a liquid and/or a gas in a treatment vessel 10 provided with: a perforated plate 18 which is placed at the bottom 9 of the vessel 10 and which discharges waste water; garbage agitation blades 16 placed inside the vessel 10; and a water spray port 12 also placed inside the vessel 10. Activated carbon fiber is added together with a core material to the garbage.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、生ごみをH2O、
CO2等の液体又は気体に生物分解する消滅型の生ごみ
処理方法に関する。
BACKGROUND OF THE INVENTION The present invention relates to a method for converting food waste into H 2 O,
The present invention relates to an extinguishable garbage disposal method that biodegrades into a liquid or gas such as CO 2 .

【0002】[0002]

【従来の技術】近年、産業が急速に発展し、都市文化が
充実するに連れ、それに伴って、生ごみ、可燃性ごみ等
の廃棄物が多量に、且つ、集中的に発生するようになっ
た。この廃棄物を処理するに当たって、可燃性ごみは主
として焼却されている。
2. Description of the Related Art In recent years, with the rapid development of industry and the enrichment of urban culture, wastes such as garbage and combustible waste have been generated in large quantities and intensively. Was. In treating this waste, combustible waste is mainly incinerated.

【0003】他方、生ごみは、微生物による分解処理が
一般的に行われており、その処理方法としてはコンポス
ト型生ごみ処理や消滅型生ごみ処理等がある。
[0003] On the other hand, garbage is generally subjected to a decomposition treatment by microorganisms, and as a treatment method, there are a compost-type garbage treatment and an extinguishable garbage treatment.

【0004】コンポスト型生ごみ処理は、生ごみを60
〜70℃の高温で処理して堆肥にするものである。
In the compost-type garbage disposal, 60 garbage can be removed.
It is treated at a high temperature of ~ 70 ° C to make compost.

【0005】これに対して、消滅型生ごみ処理は、籾殻
等をコア材(菌床)として用い、生ごみを20〜40℃
の低温でH2O、CO2等の液体又は気体に生物分解する
ものである。しかも、消滅型生ごみ処理は、繰返し使用
するコア材以外は固形物が殆ど残らないことを特徴とす
る。また、籾殻等のコア材にゼオライトを添加して生ご
みを処理すること(特許第3046703号公報)、あ
るいは前記コア材に特殊微生物を入れて生ごみを処理す
ることにより、消滅型生ごみ処理における分解活性を更
に高いものにすることができる。
[0005] On the other hand, the extinguishable garbage treatment uses rice husks or the like as a core material (bacterial bed) and removes garbage at 20 to 40 ° C.
Biodegrades into liquids or gases such as H 2 O and CO 2 at low temperatures. Moreover, the extinguishable garbage disposal is characterized in that almost no solid matter remains except for the core material used repeatedly. In addition, the processing of garbage by adding zeolite to a core material such as rice hulls (Patent No. 30467703), or by processing a garbage by adding a special microorganism to the core material, can eliminate garbage. Can further increase the decomposition activity.

【0006】しかし、これらの従来の消滅型生ごみ処理
は、生ごみの液体又は気体への分解活性が高い反面、分
解によって生ずる排水のCOD値(化学的酸素要求量)
が高い値となってしまうという問題点がある。例えば約
18000ppmと高くなってしまう場合さえあって、
この高いCOD値の排水をも処理しなければならないと
いう問題点がある。生ずる排水のCOD値を低くするに
は、処理中の生ごみへの給水量を多くすることにより生
ごみの分解活性を低く抑える方法が考えられる。しか
し、給水量を多くすると、水の使用量及び排水量が多く
なって不経済であるばかりか、破砕された細かいごみが
公共下水道や河川等の系外に流出してしまうという問題
点がある。
However, these conventional extinction-type garbage treatments have a high activity of decomposing garbage into liquid or gas, but have a COD value (chemical oxygen demand) of wastewater generated by decomposition.
Has a high value. For example, it may be as high as about 18000 ppm,
There is a problem that the wastewater having such a high COD value must be treated. In order to lower the COD value of the generated wastewater, a method of suppressing the decomposition activity of the garbage by increasing the amount of water supplied to the garbage being treated is conceivable. However, when the amount of supplied water is increased, the amount of used water and the amount of drainage are increased, which is not only uneconomical, but also has a problem that crushed fine waste flows out of the system such as a public sewer or a river.

【0007】[0007]

【発明が解決しようとする課題】本発明者は、上記問題
を解決するために種々検討した結果、消滅型生ごみ処理
において、籾殻等のコア材に活性炭素繊維(ACF)を
添加したコア材を用いて生ごみを処理することにより、
生ごみの液体又は気体への分解活性が高いばかりでな
く、処理中の生ごみへの給水量を多くすることなく、分
解によって生ずる排水のCOD値を低くできることを知
得し、本発明を完成するに至った。
As a result of various studies to solve the above problems, the present inventor has found that a core material obtained by adding activated carbon fiber (ACF) to a core material such as rice hulls in an extinguishable garbage treatment. By processing garbage using
Completed the present invention by not only having a high activity of decomposing garbage into liquid or gas, but also reducing the COD value of wastewater generated by decomposition without increasing the amount of water supplied to garbage during treatment. I came to.

【0008】従って、本発明の目的とするところは、上
記問題を解決した生ごみの処理方法を提供することにあ
る。
Accordingly, it is an object of the present invention to provide a method of treating garbage which has solved the above-mentioned problems.

【0009】[0009]

【課題を解決するための手段】上記目的を達成する本発
明は、以下に記載するものである。
The present invention to achieve the above object is as described below.

【0010】〔1〕 処理槽の底部に排水用多孔板を備
えると共に処理槽の内部に生ごみ攪拌翼と散水口を有す
る処理槽内で生ごみを液体又は気体に生物分解する生ご
みの処理方法において、生ごみにコア材と共に活性炭素
繊維を添加することを特徴とする生ごみの処理方法。
[1] Treatment of garbage in which a perforated plate for drainage is provided at the bottom of the treatment tank and the garbage is biodegraded into liquid or gas in a treatment tank having a garbage stirring blade and a water spout inside the treatment tank. A method for treating garbage, comprising adding activated carbon fibers together with a core material to the garbage.

【0011】〔2〕 攪拌翼の駆動及び散水を断続的に
行う〔1〕に記載の生ごみの処理方法。
[2] The method for treating garbage according to [1], wherein the stirring blades are driven and water is intermittently driven.

【0012】〔3〕 活性炭素繊維の添加量がコア材と
活性炭素繊維の合計添加量に対して5〜20質量%であ
る〔1〕に記載の生ごみの処理方法。
[3] The method for treating garbage according to [1], wherein the added amount of the activated carbon fibers is 5 to 20% by mass based on the total added amount of the core material and the activated carbon fibers.

【0013】〔4〕 コア材が籾殻である〔1〕に記載
の生ごみの処理方法。
[4] The method for treating garbage according to [1], wherein the core material is rice husk.

【0014】[0014]

【発明の実施の形態】以下、図面を参照して本発明を詳
細に説明する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below in detail with reference to the drawings.

【0015】図1乃至4は、本発明の生ごみの処理方法
に用いる装置の一例を示す概略図である。図1は、生ご
み処理装置の平面図を示す概略図である。図2は、生ご
み処理装置の正面図を示す概略図である。図3は、断面
部分が図1におけるA〜A断面に相当する断面部分であ
る正面部分断面図を示す概略図である。図4は、断面部
分が図1におけるB〜B断面に相当する断面部分である
側面部分断面図を示す概略図である。
FIGS. 1 to 4 are schematic views showing an example of an apparatus used in the method for treating garbage according to the present invention. FIG. 1 is a schematic view showing a plan view of the garbage processing apparatus. FIG. 2 is a schematic view showing a front view of the garbage processing apparatus. FIG. 3 is a schematic view showing a front partial cross-sectional view in which the cross-sectional portion is a cross-sectional portion corresponding to the cross section A to A in FIG. FIG. 4 is a schematic diagram showing a partial side cross-sectional view in which the cross-sectional portion is a cross-sectional portion corresponding to the cross section BB in FIG.

【0016】この処理装置において、図3中、2は筺状
の外枠で、外枠2の上面には蓋4が設けられている。外
枠2の内部には内枠6が設けられている。内枠6の上部
は開放され、その上縁部で外枠2の内壁上部に設けられ
た支持枠8に固定されている。内枠6の内部には断熱材
が充填されている。内枠6の底部9は断面U字形で、前
記内枠6と共に処理槽10を構成している。処理槽10
の内部の頂部付近には外枠2及び内枠6を貫通して処理
槽10の内部に挿入された水管の散水口12が設けられ
ている。
In this processing apparatus, reference numeral 2 in FIG. 3 denotes an outer frame of a housing, and a lid 4 is provided on the upper surface of the outer frame 2. An inner frame 6 is provided inside the outer frame 2. The upper part of the inner frame 6 is opened, and the upper edge thereof is fixed to a support frame 8 provided on the upper part of the inner wall of the outer frame 2. The inside of the inner frame 6 is filled with a heat insulating material. A bottom portion 9 of the inner frame 6 has a U-shaped cross section, and constitutes a processing tank 10 together with the inner frame 6. Processing tank 10
A water sprinkling port 12 of a water pipe inserted through the outer frame 2 and the inner frame 6 and inserted into the inside of the processing tank 10 is provided near the top of the inside.

【0017】処理槽10の内部中心部分には攪拌軸14
が横設されている。攪拌軸14には複数(本例において
は6本)の攪拌翼16が分散配置されている。
A stirring shaft 14 is provided at the center of the inside of the processing tank 10.
Is installed horizontally. A plurality (six in this example) of stirring blades 16 are dispersedly arranged on the stirring shaft 14.

【0018】処理槽10の底部9の最下部は多孔板18
で形成されている。多孔板18の下方には排水樋20が
設けられ、排水樋20の一端には排水管23が設けられ
ている。排水樋20は排水管23側の端が最も低くなる
ように傾斜がつけられている。
The bottom of the bottom 9 of the processing tank 10 is
It is formed with. A drain gutter 20 is provided below the perforated plate 18, and a drain pipe 23 is provided at one end of the drain gutter 20. The drain gutter 20 is inclined so that the end on the drain pipe 23 side is the lowest.

【0019】処理槽10の底部9の下方であって、排水
樋20の両側方には、ヒーター24が設けられ、ヒータ
ー24の下方には反射板26が設けられている。
A heater 24 is provided below the bottom 9 of the treatment tank 10 and on both sides of the drain gutter 20, and a reflector 26 is provided below the heater 24.

【0020】なお、攪拌軸14は、内枠6を貫通して、
軸支されると共に、その軸端に、Vベルト等の動力伝達
装置(不図示)を介して攪拌モーター28の動力が伝達
される。30は制御パネルで、これにより本装置が操作
される。
The stirring shaft 14 penetrates through the inner frame 6 and
The power of the stirring motor 28 is transmitted to a shaft end via a power transmission device (not shown) such as a V-belt. Reference numeral 30 denotes a control panel, by which the apparatus is operated.

【0021】本発明の生ごみ処理方法の一形態は、処理
槽10においてコア材を用いて生ごみを液体又は気体に
生物分解処理するに当たって、コア材と共に活性炭素繊
維を添加するものである。
In one embodiment of the method for treating garbage of the present invention, activated carbon fibers are added together with the core material when the garbage is biodegraded into liquid or gas using the core material in the treatment tank 10.

【0022】この消滅型生ごみ処理方法において、コア
材と共に添加する活性炭素繊維としては繊維径1mm以
下、好ましくは0.001〜500μmに紡糸した後、
炭化、賦活した活性炭素繊維であれば、長繊維でも短繊
維でも好ましく用いることができる。
In this method, the activated carbon fibers added together with the core material are spun to a fiber diameter of 1 mm or less, preferably 0.001 to 500 μm.
As long as activated carbon fibers are carbonized and activated, either long fibers or short fibers can be preferably used.

【0023】ここで、例えば活性炭のような粒状のもの
は、処理槽10における生ごみの攪拌処理中に破砕され
やすく処理液(排水)と共に流出し、再使用が困難であ
ったり、処理中での補給を必要としたりするので好まし
くない。
Here, particulate matter such as activated carbon, for example, is easily crushed during the agitation treatment of garbage in the treatment tank 10 and flows out together with the treatment liquid (drainage), and it is difficult to reuse it or during treatment. It is not preferable because replenishment is required.

【0024】なお、活性炭素繊維は、紡糸した後、炭
化、賦活したものであれば、比表面積は特に限定される
ものではないが、300〜2000m2/gが好まし
い。
The specific surface area of the activated carbon fiber is not particularly limited as long as it is carbonized and activated after spinning, but it is preferably 300 to 2000 m 2 / g.

【0025】本発明の生ごみ処理方法において、生ごみ
にコア材と共に添加する活性炭素繊維の添加量は、コア
材と活性炭素繊維の合計添加量に対して5〜20質量%
であることが好ましい。
In the method for treating garbage according to the present invention, the amount of the activated carbon fiber added to the garbage together with the core material is 5 to 20% by mass based on the total amount of the core material and the activated carbon fiber.
It is preferred that

【0026】活性炭素繊維の添加量が5質量%未満の場
合は、生ごみの分解によって生ずる排水のCOD値が高
くなるので好ましくなく、一方、活性炭素繊維の添加量
が20質量%を超える場合は、活性炭素繊維の添加量が
多い割には生ごみの分解によって生ずる排水のCOD値
は低くならないので好ましくない。
When the amount of the activated carbon fiber is less than 5% by mass, the COD value of the wastewater generated by the decomposition of garbage becomes high, which is not preferable. On the other hand, when the amount of the activated carbon fiber exceeds 20% by mass. Is not preferable because the COD value of the wastewater generated by the decomposition of garbage does not become low even though the added amount of the activated carbon fiber is large.

【0027】本発明の生ごみ処理方法に用いるコア材と
しては、籾殻、そば殻、カンナクズ、並びに、木質細片
及び樹皮等の木材チップが好ましい。なお、大鋸屑は処
理槽10における生ごみの攪拌処理中に破砕されやすく
処理液(排水)と共に流出し、再使用が困難であった
り、処理中での補給を必要としたりするので好ましくな
い。
As the core material used in the garbage disposal method of the present invention, rice husks, buckwheat husks, kanakus, and wood chips such as wood chips and bark are preferable. In addition, the sawdust is liable to be crushed during the agitation treatment of the garbage in the treatment tank 10 and flows out together with the treatment liquid (drainage), which is not preferable because it is difficult to reuse or needs to be replenished during the treatment.

【0028】図1乃至4に示す生ごみ処理装置におい
て、蓋4から処理槽10内に、生ごみ、コア材、及び活
性炭素繊維を投入する。これらの投入物は攪拌翼16の
間欠運転によって攪拌混合され、散水口12からの間欠
散水、及びヒーター24での加熱によって反応温度等の
調整がなされ、生ごみの分解処理が行われる。
In the garbage processing apparatus shown in FIGS. 1 to 4, garbage, a core material, and activated carbon fibers are put into the processing tank 10 from the lid 4. These input materials are stirred and mixed by intermittent operation of the stirring blade 16, the reaction temperature and the like are adjusted by intermittent watering from the water spouting port 12 and heating by the heater 24, and the decomposition of garbage is performed.

【0029】処理槽10における攪拌翼16の駆動は断
続的に行うことが好ましく、攪拌時間は0.1〜30分
が好ましく、0.5〜10分が更に好ましい。攪拌停止
時間は1〜200分が好ましい。
The stirring blade 16 in the processing tank 10 is preferably driven intermittently, and the stirring time is preferably from 0.1 to 30 minutes, more preferably from 0.5 to 10 minutes. The stirring stop time is preferably from 1 to 200 minutes.

【0030】処理槽10における間欠散水については、
散水時間は1〜200秒が好ましい。散水停止時間は
0.5〜120分が好ましい。
Regarding intermittent watering in the treatment tank 10,
Watering time is preferably 1 to 200 seconds. The watering stop time is preferably 0.5 to 120 minutes.

【0031】生ごみの分解によって生じた排水は、処理
槽10の底部9の多孔板18から排水樋20、排水管2
3を通って系外に排出される。多孔板18に穿設された
孔の径は、コア材、活性炭素繊維等の形状や大きさによ
って適宜選ぶことができるが、0.01〜5mmが好ま
しく、0.1〜2mmが更に好ましい。
The waste water generated by decomposition of the garbage is discharged from the perforated plate 18 at the bottom 9 of the treatment tank 10 to the drain gutter 20 and the drain pipe 2.
It is discharged out of the system through 3. The diameter of the holes formed in the perforated plate 18 can be appropriately selected depending on the shape and size of the core material, the activated carbon fibers, and the like, but is preferably 0.01 to 5 mm, more preferably 0.1 to 2 mm.

【0032】本発明に用いられる生ごみ処理槽は、散水
口、攪拌翼、及び多孔板を備えた処理槽であることを特
徴とする。しかし、散水口、攪拌翼、及び多孔板は、そ
れぞれ、生ごみに散水する手段、生ごみを攪拌する手
段、及び生ごみの分解によって生じた排水を濾過する手
段であれば良く、必ずしも散水口、攪拌翼、及び多孔板
に限定されるものではない。
The garbage treatment tank used in the present invention is characterized by being a treatment tank provided with a water spout, a stirring blade, and a perforated plate. However, the water spout, the stirring blade, and the perforated plate may be any means for sprinkling the garbage, for stirring the garbage, and for filtering the wastewater generated by the decomposition of the garbage, respectively. , Stirring blades, and perforated plates.

【0033】[0033]

【実施例】以下、本発明を実施例により、具体的且つ詳
細に説明するが、本発明は実施例により限定されるもの
ではない。
EXAMPLES Hereinafter, the present invention will be described specifically and in detail with reference to examples, but the present invention is not limited to the examples.

【0034】なお、生ごみ処理装置は、図1乃至4の概
要図に示す東邦化工建設株式会社製内容積80L(リッ
トル)の生ごみ処理装置を用いた。
The garbage processing apparatus used was a garbage processing apparatus having an internal volume of 80 L (liter) manufactured by Toho Kako Construction Co., Ltd. shown in the schematic diagrams of FIGS.

【0035】実施例1 本実施例に用いた生ごみの組成を表1に示す。Example 1 Table 1 shows the composition of garbage used in this example.

【0036】[0036]

【表1】 [Table 1]

【0037】図1乃至4に示す生ごみ処理装置におい
て、表1に示す生ごみ1.9kgと共に、表2の実施例
1に示す量の籾殻、及び活性炭素繊維(比表面積120
0m2/g)を、内容積80Lの処理槽10に投入し
た。
1 to 4 together with 1.9 kg of garbage shown in Table 1 together with the amount of rice hulls and activated carbon fibers (specific surface area of 120 kg) shown in Example 1 of Table 2.
0 m 2 / g) was charged into the processing tank 10 having an internal volume of 80 L.

【0038】処理槽10における攪拌は、攪拌時間2
分、攪拌停止時間15分を繰り返すことによって行っ
た。処理槽10における散水は、散水時間15秒、散水
停止時間10分を繰り返すことによって行い、1日当た
りの散水量は96Lとした。なお、処理槽10内の温度
は35℃に調整した。
The stirring in the processing tank 10 is performed for a stirring time of 2 hours.
And stirring stop time of 15 minutes was repeated. Watering in the treatment tank 10 was performed by repeating a watering time of 15 seconds and a watering stop time of 10 minutes, and the watering amount per day was 96 L. In addition, the temperature in the processing tank 10 was adjusted to 35 ° C.

【0039】以上の条件により生ごみの分解処理を行
い、所定の処理時間ごとに分解によって生じた排水のC
ODを測定し、図5に示す結果を得た。
The garbage is decomposed under the above conditions, and the wastewater generated by the decomposition is decomposed every predetermined time.
OD was measured, and the result shown in FIG. 5 was obtained.

【0040】比較例1 表2の比較例1に示す条件で、実施例1の場合と同様に
生ごみの分解処理を行い、図5に示す結果を得た。
COMPARATIVE EXAMPLE 1 Under the conditions shown in Comparative Example 1 in Table 2, the garbage was decomposed in the same manner as in Example 1, and the results shown in FIG. 5 were obtained.

【0041】[0041]

【表2】 [Table 2]

【0042】図5の結果に示すように、比較例1の場合
は、生ごみ処理槽に投入したものは籾殻だけで活性炭素
繊維は投入しておらず、排水のCODが高く、最高で1
8000ppmにも達した。
As shown in the results of FIG. 5, in the case of Comparative Example 1, only the rice husk was charged into the garbage treatment tank without the activated carbon fiber, and the COD of the wastewater was high.
It reached 8000 ppm.

【0043】これに対して、実施例1の場合は、活性炭
素繊維の生ごみ処理槽への投入量がコア材と活性炭素繊
維の合計投入量に対して9質量%であって、排水のCO
Dを最高でも4000ppmにまで低減することができ
たことが解る。
On the other hand, in the case of Example 1, the input amount of the activated carbon fiber into the garbage disposal tank was 9% by mass based on the total input amount of the core material and the activated carbon fiber, and CO
It can be seen that D could be reduced to at most 4000 ppm.

【0044】また、比較例1の場合は、生ごみ分解処理
の最初の24時間における排水のCODは平均で470
0ppmと、実施例1の場合における排水のCODの最
高値4000ppmよりも高い値であった。なお、実施
例1の場合における排水のCODの最初の24時間にお
ける平均値は2200ppmと極めて低い値であった。
In the case of Comparative Example 1, the COD of the wastewater in the first 24 hours of the garbage decomposition treatment was 470 on average.
It was 0 ppm, which was higher than the maximum value of 4000 ppm of COD of the wastewater in the case of Example 1. In the case of Example 1, the average value of the COD of the wastewater in the first 24 hours was an extremely low value of 2200 ppm.

【0045】[0045]

【発明の効果】本発明の生ごみの処理方法によれば、コ
ア材を用いて生ごみを液体又は気体に生物分解処理する
に当たって、コア材と共に活性炭素繊維を添加している
ので、生ごみの液体又は気体への分解活性が高いばかり
でなく、処理中の生ごみへの給水量を多くすることな
く、生ごみの分解によって生ずる排水のCODを低く抑
えることができる。
According to the method for treating garbage according to the present invention, activated carbon fibers are added together with the core material when the garbage is biodegraded into a liquid or a gas using the core material. Not only has a high activity of decomposing garbage into liquid or gas, but also does not increase the amount of water supplied to garbage during treatment, and can reduce COD of wastewater generated by decomposition of garbage.

【0046】活性炭素繊維は柔軟性に富み、通常の粒状
又は破砕状活性炭と比較して破砕され難いので、多孔板
の孔を通って外部に流出することがなく長期間の使用に
耐える。
Activated carbon fibers are rich in flexibility and hard to be crushed as compared with ordinary granular or crushed activated carbon, and thus can be used for a long time without flowing out through the holes of the perforated plate.

【0047】更に、給水量を少なく抑えると、水の使用
量及び排水量を少なく抑えることができ、経済的であ
る。しかも、生ごみは液体又は気体まで急速に分解され
るので、分解途中の破砕された細かいごみが公共下水道
や河川等の系外に流出してしまうこともなくなる。
Further, if the amount of supplied water is reduced, the amount of water used and the amount of drainage can be reduced, which is economical. Moreover, since the garbage is rapidly decomposed into a liquid or a gas, the crushed fine garbage that is being decomposed does not flow out of the system such as a public sewer or a river.

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

【図1】本発明の生ごみの処理方法に用いる装置の一例
を示す概略図であって、同装置の平面図を示す概略図で
ある。
FIG. 1 is a schematic view showing an example of an apparatus used in the method for treating garbage of the present invention, and is a schematic view showing a plan view of the apparatus.

【図2】本発明の生ごみの処理方法に用いる装置の一例
を示す概略図であって、同装置の正面図を示す概略図で
ある。
FIG. 2 is a schematic view showing an example of an apparatus used in the method for treating garbage of the present invention, and is a schematic view showing a front view of the apparatus.

【図3】断面部分が図1におけるA〜A断面に相当する
断面部分である正面部分断面図を示す概略図である。
FIG. 3 is a schematic diagram showing a front partial cross-sectional view in which a cross-sectional portion is a cross-sectional portion corresponding to the cross section A to A in FIG. 1;

【図4】断面部分が図1におけるB〜B断面に相当する
断面部分である側面部分断面図を示す概略図である。
FIG. 4 is a schematic diagram showing a side partial cross-sectional view in which the cross-sectional portion is a cross-sectional portion corresponding to the cross section BB in FIG. 1;

【図5】実施例1及び比較例1の生ごみ分解処理試験結
果における処理時間と排水のCODとの関係を示すグラ
フである。
FIG. 5 is a graph showing the relationship between treatment time and COD of wastewater in the results of the garbage decomposition test of Example 1 and Comparative Example 1.

【符号の説明】[Explanation of symbols]

2 外枠 4 蓋 6 内枠 8 支持枠 9 処理槽の底部 10 処理槽 12 散水口 14 攪拌軸 16 攪拌翼 18 多孔板 20 排水樋 23 排水管 24 ヒーター 26 反射板 28 攪拌モーター 30 制御パネル 2 outer frame 4 lid 6 inner frame 8 support frame 9 bottom of processing tank 10 processing tank 12 water spouting port 14 stirring shaft 16 stirring blade 18 perforated plate 20 drainage gutter 23 drainage pipe 24 heater 26 reflector 26 stirring motor 30 control panel

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D004 AA03 CA13 CA15 CA19 CA22 CB02 CB06 CB28 CB32 CC03 CC08 CC11 DA02 DA03 DA10 DA13 4G078 AA06 AA21 AB20 BA01 BA09 CA01 CA05 CA12 CA17 DA01 DB01 EA10 EA13  ──────────────────────────────────────────────────続 き Continued on the front page F term (reference) 4D004 AA03 CA13 CA15 CA19 CA22 CB02 CB06 CB28 CB32 CC03 CC08 CC11 DA02 DA03 DA10 DA13 4G078 AA06 AA21 AB20 BA01 BA09 CA01 CA05 CA12 CA17 DA01 DB01 EA10 EA13

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 処理槽の底部に排水用多孔板を備えると
共に処理槽の内部に生ごみ攪拌翼と散水口を有する処理
槽内で生ごみを液体又は気体に生物分解する生ごみの処
理方法において、生ごみにコア材と共に活性炭素繊維を
添加することを特徴とする生ごみの処理方法。
1. A method of treating garbage in which a garbage is biodegraded into a liquid or a gas in a treatment tank having a perforated plate for drainage at the bottom of the treatment tank and having a garbage stirring blade and a water spout inside the treatment tank. 3. A method for treating garbage, wherein activated carbon fibers are added to the garbage together with the core material.
【請求項2】 攪拌翼の駆動及び散水を断続的に行う請
求項1に記載の生ごみの処理方法。
2. The method for treating garbage according to claim 1, wherein the stirring blade is driven intermittently and watering is performed intermittently.
【請求項3】 活性炭素繊維の添加量がコア材と活性炭
素繊維の合計添加量に対して5〜20質量%である請求
項1に記載の生ごみの処理方法。
3. The method for treating garbage according to claim 1, wherein the added amount of the activated carbon fiber is 5 to 20% by mass based on the total added amount of the core material and the activated carbon fiber.
【請求項4】 コア材が籾殻である請求項1に記載の生
ごみの処理方法。
4. The method for treating garbage according to claim 1, wherein the core material is rice husk.
JP2000380865A 2000-12-14 2000-12-14 Garbage treatment process Pending JP2002177930A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000380865A JP2002177930A (en) 2000-12-14 2000-12-14 Garbage treatment process

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000380865A JP2002177930A (en) 2000-12-14 2000-12-14 Garbage treatment process

Publications (1)

Publication Number Publication Date
JP2002177930A true JP2002177930A (en) 2002-06-25

Family

ID=18848981

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000380865A Pending JP2002177930A (en) 2000-12-14 2000-12-14 Garbage treatment process

Country Status (1)

Country Link
JP (1) JP2002177930A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2016068075A (en) * 2014-09-30 2016-05-09 Sinkpia・Japan株式会社 Garbage disposer and management system of the same

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2016068075A (en) * 2014-09-30 2016-05-09 Sinkpia・Japan株式会社 Garbage disposer and management system of the same

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