JPS63156585A - Method and device for controlling development of rancidity from waste perishables - Google Patents

Method and device for controlling development of rancidity from waste perishables

Info

Publication number
JPS63156585A
JPS63156585A JP61302595A JP30259586A JPS63156585A JP S63156585 A JPS63156585 A JP S63156585A JP 61302595 A JP61302595 A JP 61302595A JP 30259586 A JP30259586 A JP 30259586A JP S63156585 A JPS63156585 A JP S63156585A
Authority
JP
Japan
Prior art keywords
activated carbon
waste
hopper
perishables
discharge mechanism
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
JP61302595A
Other languages
Japanese (ja)
Inventor
Yutaka Ota
豊 太田
Toshiaki Yoshida
吉田 稔秋
Keisuke Kawaguchi
川口 恵右
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.)
Mitsui Construction Co Ltd
Kansai Coke and Chemicals Co Ltd
Original Assignee
Mitsui Construction Co Ltd
Kansai Coke and Chemicals 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 Mitsui Construction Co Ltd, Kansai Coke and Chemicals Co Ltd filed Critical Mitsui Construction Co Ltd
Priority to JP61302595A priority Critical patent/JPS63156585A/en
Publication of JPS63156585A publication Critical patent/JPS63156585A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To control the development of rancidity from a pile of waste perishables before being burned, by mixing activated carbon into the waste perishables. CONSTITUTION:A hopper 1 for receiving waste perishables, a waste perishables discharge mechanism 2 connected to the bottom opening of the receiving hopper 1, an activated carbon hopper 3 for supplying activated carbon to the waste perishables traveling in the discharge mechanism 2 provided midway of the discharge mechanism 2, and a quantitative feeder 4 for activated carbon provided at the bottom opening of the hopper 3 are furnished. A fixed amt. of activated carbon is mixed into the waste perishables traveling in the discharged mechanism 2 from the activated carbon feeder 3, and the waste is discharged to the outside of the system. As a result, the development of rancidity from a pile of waste perishables before being burned can be controlled.

Description

【発明の詳細な説明】 [産業上の利用分野1 本発明は、家庭の台所、ホテル、飲食業等より発生する
大量の生ごみ、海中に水没する海洋構造物から除去され
た貝類等の生鮮廃棄物の堆積物から発生する臭気を抑制
する方法およびその方法を実施するための装置に関する
ものであり、生鮮廃棄物の堆積場に適用すれば、それよ
り発生する悪臭の発散が抑制され、悪臭公害が未然に防
止され、周辺の生活環境が改善される等の効果がある。
[Detailed Description of the Invention] [Industrial Application Field 1] The present invention is applicable to large amounts of food waste generated from home kitchens, hotels, restaurant businesses, etc., and fresh waste such as shellfish removed from marine structures submerged in the sea. This article relates to a method for suppressing odors generated from waste piles and a device for carrying out the method.If applied to a fresh waste dump, the emission of bad odors generated from the piles can be suppressed and odor pollution can be prevented. This has the effect of preventing accidents and improving the living environment in the surrounding area.

[従来の技術] 海岸線に沿って立地された工場においては、工場内での
熱交換のため、海水が冷却用水として大口に使用される
ことがおる。このような場合、冷却用海水は、海水に向
って開口する取水口から取り入れられるのでおるが、こ
の取水口付近、および海水通路の内壁には、例えば、む
らさき貝や、ふじつぼ等の貝類が付着する。そして、そ
の繁殖が盛んになると層をなして、通路内壁を覆ってし
まうことから海水通路がせまくなり、あるいはその死骸
が剥れ、工場内熱交換器等の諸施設の配管内を閉塞して
しまうという事態が発生する。
[Prior Art] In factories located along the coastline, large quantities of seawater are sometimes used as cooling water for heat exchange within the factory. In such cases, the cooling seawater is taken in through the water intake that opens toward the seawater, but there are shellfish such as purple shellfish and barnacles near the water intake and on the inner walls of the seawater passage. adhere to. When they multiply, they form a layer and cover the inner walls of the passage, making the seawater passage narrower, or their carcasses peel off and block the pipes of various facilities such as the factory heat exchanger. A situation arises where it is put away.

そこで、これを解消するために、定期的に潜水夫が上記
海水通路内に潜って、貝類を除去し、それを地上に一時
的に野積みすることが行われる。
To solve this problem, divers periodically dive into the seawater passageway to remove shellfish and temporarily pile them up on the ground.

野積みされた貝類は、ある程度まとまったところで、焼
却場に運ばれ、焼却処理されるのであるが、その間、貝
類は腐敗し、野積み堆積物からは強烈な腐敗臭が発生し
、周辺の生活環境を害する。
Once the shellfish piled up in the open are gathered to a certain extent, they are transported to an incinerator and incinerated. During this time, the shellfish rot and a strong odor of decay is emitted from the piled pile, which is harmful to the surrounding life. harm the environment;

従来、このような悪臭の発生に対処するために、芳香を
発するマスキング剤を上記堆積物に振りかけるとか、臭
気をフード等で集め、後方の脱臭設備で脱臭してのち集
気を大気中に放出することが行なわれていた。しかしな
がら前者にあっては、顕著な効果は得られず、又、後者
にあっては黄火な設備投資が必要であるという不都合が
あった。
Conventionally, in order to deal with the occurrence of such bad odors, the above-mentioned deposits were sprinkled with a masking agent that emits an aroma, or the odors were collected with a hood, etc., and the collected air was deodorized with deodorizing equipment at the rear, and then the collected air was released into the atmosphere. Something was being done. However, the former method does not produce any significant effects, and the latter method requires significant capital investment.

[発明が解決しようとする問題点コ 本発明は、焼却処理に至るまでの堆積中に生鮮廃棄物か
ら発生する腐敗臭気を抑制する方法およびその装置を提
供することを目的とする。
[Problems to be Solved by the Invention] An object of the present invention is to provide a method and an apparatus for suppressing putrid odors generated from perishable waste during accumulation up to incineration.

[問題を解決するための手段] 本発明は、前記のような問題を解決するために、鋭意検
討の結果なされたものである。しかして、第1の発明は
、生鮮廃棄物に活性炭を混入することを要旨とするもの
である。また、第2の発明は、この方法を実施するため
に用いられる装置であって、生鮮廃棄物の投入される受
入れホッパー、該受入れホッパー底面開口部と接続する
生鮮廃棄物排出機構、該排出機構の途中に設けられる排
出は構内を移動中の生鮮廃棄物に活性炭を供給する活性
炭ホッパー、および該ホッパー底面開口部に設けられた
活性炭の定量切出し装置とを備え、前記排出機構内を移
動中の生鮮廃棄物に活性炭ホッパーから一定量の活性炭
を混入して、系外に排出するようにした生鮮廃棄物から
発生する臭気を抑制する装置を要旨とするものである。
[Means for Solving the Problems] The present invention has been made as a result of intensive studies in order to solve the above problems. Therefore, the gist of the first invention is to mix activated carbon into perishable waste. Further, a second invention is an apparatus used for carrying out this method, which comprises a receiving hopper into which perishable waste is thrown, a perishable waste discharge mechanism connected to the bottom opening of the receiving hopper, and the discharge mechanism. The discharge mechanism installed in the middle of the discharge mechanism is equipped with an activated carbon hopper that supplies activated carbon to the perishable waste that is being moved within the premises, and an activated carbon quantitative cutting device that is installed at the bottom opening of the hopper. The gist of this device is to suppress the odor generated from perishable waste by mixing a certain amount of activated carbon into the perishable waste from an activated carbon hopper and discharging it outside the system.

本発明をざらに説明するに、本発明に用いられる活性炭
は、椰子殻、石炭あるいは木材等の炭素源を原料とし、
それに水蒸気または薬剤等を添加して賦活後、得られる
ミクロポ1−の発達した所謂通常の活性炭であれば、ど
のようなものでもよく、特に限定されるものではない。
To briefly explain the present invention, the activated carbon used in the present invention is made from carbon sources such as coconut shells, coal, or wood;
There is no particular limitation, and any type of activated carbon may be used as long as it is a so-called normal activated carbon in which micropores are developed after activation by adding water vapor or a chemical or the like.

また、活性炭は粉末炭(通常100メツシユパスが80
%以上あるもの)と粒状炭とがあるが、そのいずれをも
適用できる。又、活性炭に鉄粉を混入しておくと、鉄の
被酸化力によって通常は活性炭で吸着除去し難い硫化水
素等の臭気成分も分解し、より効果的に臭気の発生を抑
制できるので具合がよい。
In addition, activated carbon is powdered charcoal (usually 100 mesh passes is 80
% or more) and granular charcoal, both of which can be applied. In addition, if iron powder is mixed into activated carbon, the oxidizability of iron will decompose odor components such as hydrogen sulfide, which are normally difficult to adsorb and remove with activated carbon, making it possible to suppress odor generation more effectively. good.

臭気抑制の対象となる生鮮廃棄物については海水取水口
で除去された貝類を先に例示したが、特に、これに限定
されるものではなく、食品製造工場で発生する廃棄物や
家庭の台所や、ホテル、レストランの調理場から゛発生
する所謂生ごみにも本発明が適用されることは言うまで
もない。
Examples of perishable waste subject to odor control include shellfish removed at seawater intakes, but the waste is not limited to this, and waste generated at food manufacturing plants and household kitchens and It goes without saying that the present invention is also applicable to so-called raw garbage generated from the kitchens of restaurants, hotels, and restaurants.

次に、本発明方法を実施するための装置をその一例を示
す第1図に基いて説明する。
Next, an apparatus for implementing the method of the present invention will be explained based on FIG. 1 showing an example thereof.

第1図において、1は生鮮廃棄物を投入する受入れホッ
パーであり、この投入は、作業者がスコップ等で直接行
ってもよいが、図示せざる例えばポータプルベルトコン
ベア等を介して行ってもよい。2は前記受入れホッパー
1の底面開口部と接続する生鮮廃棄物の排出機構であり
、受入れホッパー1内の廃棄物を系外に排出するための
ものでおる。第1図の例では、排出機構としてスクリュ
ーコンベアを内装するものが示されているが、特にこれ
に限定されるものではなく、ベルトコンベア等地の移送
手段のものであってもよい。該排出機構2は排出口5に
向って上昇するように傾斜かつけられているが、これは
、排出口5から落下する処理済廃棄物の堆積物6の堆積
面積をできるだけせまくして、ある程度の高ざまで積上
げ可能とするためである。排出機構2内のスクリューコ
ンベアの軸7の回転は、排出機構2の後方に同軸で設け
られた駆動装置8により行われる。なありは、可変速機
であって、駆動装置8の回転を予め設定された割合で減
速させるためのものである。
In Fig. 1, reference numeral 1 denotes a receiving hopper into which perishable waste is input, and this input may be carried out directly by an operator using a shovel or the like, but it may also be carried out via a porta-pull belt conveyor, etc. (not shown). . 2 is a perishable waste discharge mechanism connected to the bottom opening of the receiving hopper 1, and is for discharging the waste in the receiving hopper 1 to the outside of the system. In the example shown in FIG. 1, a screw conveyor is installed as the discharge mechanism, but the present invention is not limited to this, and other conveying means such as a belt conveyor may be used. The discharge mechanism 2 is inclined or attached so as to rise toward the discharge port 5, but this is done in order to minimize the area in which the deposits 6 of treated waste falling from the discharge port 5 accumulate. This is to make it possible to stack them up to a height of . The shaft 7 of the screw conveyor in the discharge mechanism 2 is rotated by a drive device 8 coaxially provided at the rear of the discharge mechanism 2 . The variable speed machine is a variable speed machine that slows down the rotation of the drive device 8 at a preset rate.

排出機構2の途中には、活性炭ホッパー3が、該ホッパ
ー3の底面開口部に設けられた定量切出し装置4を介し
て接続されている。すなわち、該ホッパー3には、活性
炭が装填され、予め設定された切出し量が移送途中の生
鮮廃棄物に添加混合されるようになっている。
An activated carbon hopper 3 is connected to the middle of the discharge mechanism 2 via a quantitative cutting device 4 provided at the bottom opening of the hopper 3. That is, the hopper 3 is loaded with activated carbon, and a preset amount of activated carbon is added to and mixed with the perishable waste being transported.

10は台座11の底部に設けられた車輪であり、該車輪
10によって本発明装置は任意の場所へ自由に移動でき
るようになっている。
Reference numeral 10 denotes wheels provided at the bottom of the pedestal 11, and the wheels 10 allow the device of the present invention to be freely moved to any desired location.

本発明装置は以上のような構成よりなり、受入れホッパ
ー1に投入された生鮮廃棄物は、予め設定された量で排
出機構2内を排出口5方向に向って移動するが、その途
中で、活性炭ホッパー3から定量切出し装置4を介して
臭気吸着作用をする活性炭が所要量供給混合され、以後
、生鮮廃棄物はその表面が活性炭に被覆されたような状
態で排出機構2内を移動し、排出口5より系外に排出さ
れ、堆積物6とされる。
The apparatus of the present invention has the above-described configuration, and the perishable waste put into the receiving hopper 1 moves in the discharge mechanism 2 in the direction of the discharge port 5 in a preset amount, but on the way, A required amount of activated carbon that acts as an odor adsorbent is supplied and mixed from an activated carbon hopper 3 via a quantitative cut-out device 4, and thereafter, the perishable waste moves through the discharge mechanism 2 in a state where its surface is coated with activated carbon. It is discharged from the system through the discharge port 5 and becomes a deposit 6.

[作用] 本発明は以上のような構成よりなるので、受入れホッパ
ーに投入された生鮮廃棄物は、排出機構内を移動するが
、その移動中に活性炭ホッパーから定量切出し装置を介
して、一定岳の活性炭が供給され、廃棄物と活性炭とは
移動しながら混合され、排気口から系外に排出される。
[Function] Since the present invention has the above-described configuration, the perishable waste put into the receiving hopper moves within the discharge mechanism, and during the movement, it is removed from the activated carbon hopper via the quantitative cutting device. of activated carbon is supplied, the waste and activated carbon are mixed while moving, and are discharged from the system through the exhaust port.

このようにして、生鮮廃棄物は活性炭と均一に混合され
るので、該廃棄物から発生する悪臭臭気成分は活性炭に
吸着されて、臭気の揮散が抑制される。
In this way, the perishable waste is uniformly mixed with the activated carbon, so the malodorous odor components generated from the waste are adsorbed by the activated carbon, and volatilization of the odor is suppressed.

[実施例] 次に本発明を実施例を挙げて説明するが、本発明は、そ
の要旨を超えない限り、以下の実施例に限定されること
はない。文中「%」とあるのは唄但%を表わす。
[Examples] Next, the present invention will be described with reference to Examples, but the present invention is not limited to the following Examples unless it exceeds the gist thereof. The ``%'' in the text represents Utatan%.

実施例1 試料として、市販されている生きたあさり貝400gr
を求め、これを200grづつに分け、一方には対試料
10%の粉末活性炭を添加混合し、使方には活性炭を添
加lず、それぞれを2Qのガラス容器に密封した。この
ときに使用した活性炭はダイアソーブF100D(三協
産、業株式会社製活性炭、商品名)であり、その物性は
、次のとおりのものである。
Example 1 400 gr of commercially available live clams as a sample
This was divided into 200g portions, powdered activated carbon was added to one portion at a rate of 10% of the sample, and activated carbon was not added to one portion, and each portion was sealed in a 2Q glass container. The activated carbon used at this time was Diasorb F100D (activated carbon manufactured by Sankyo Sangyo Co., Ltd., trade name), and its physical properties were as follows.

粒度  100メツシユパス 99% 水分             6.2%ヨウ素吸着力
      1100mM+;+rメチレンブルー脱色
力   200mg/肛前記密封試料を3日間常温(約
20 ’C)で放置し、その後、ガラス容器内の気体を
採取して、主な臭気成分の濃度を測定した。なあ、臭気
成分の測定は(株)ガスチック社製のガス検知管直続式
ガス検知器セット(品番No、850シヨルダーバツク
型)を用いて行った。結果を第1表に示す。
Particle size 100 mesh pass 99% Moisture 6.2% Iodine adsorption power 1100mM +; , the concentrations of the main odor components were measured. The odor components were measured using a gas detector set (product number: 850 shoulder bag type) manufactured by Gastic Co., Ltd. with a direct connection to a gas detector tube. The results are shown in Table 1.

第1表 以上の結果から明らかなとおり、アンモニアについては
、両者変りはないが、トリメチルアミンについては、活
性炭無添加の場合に較べ、活性炭添加の場合、発散が大
巾に抑制されている。また、上記三臭気成分のうちで、
最も強烈な臭気成分であるメチルメルカプタンについて
は、活性炭無添加の場合、1.6ppmであるのが活性
炭添加の場合は、検出できない程度に発散が抑制されて
おり、生鮮廃棄物に活性炭を混入すれば、臭気の発生を
抑制する効果があることが判る。なお、実際に両者の臭
気を嗅いでみたところ、活性炭無添加のものは、嗅ぐに
耐えない猛烈な腐敗臭が感ぜられたのに対し、活性炭を
添加したものは、佃煮のようなアミン臭が若干窓ぜられ
たが、不快臭という程のものではなかった。
As is clear from the results shown in Table 1, there is no difference between the two cases regarding ammonia, but the emission of trimethylamine is significantly suppressed when activated carbon is added compared to when activated carbon is not added. Also, among the three odor components mentioned above,
Regarding methyl mercaptan, which is the most intense odor component, when activated carbon is not added, the emission is 1.6 ppm, but when activated carbon is added, the emission is suppressed to an undetectable level. For example, it can be seen that there is an effect of suppressing the generation of odor. When I actually smelled the odors of both, I found that the one without activated carbon had a strong putrid odor that was unbearable to smell, but the one with activated carbon had an amine odor similar to that of tsukudani. Although the window was slightly broken, it was not an unpleasant odor.

実施例2 実施例1で示した3日間密封放置後の活性炭添加試料に
、実施例1で用いたものと同一の活性炭を対試料1%、
4%、5%(合計10%〉と順次追加添加して、そのと
き発生した臭気成分を実施例1の場合と同様の方法で測
定した。なおその測定は、それぞれ活性炭添加後1時間
経過してから行った。また、1%添加時および4%添加
時には、ガラス棒で試料と活性炭とをガラス棒で掻き混
ぜる程度の混合を行ったが、5%追加添加時には、活性
炭をガラス容器内に装入後、密閉して容器角、数分間強
撮した。結果を第2表に示す。
Example 2 The same activated carbon as used in Example 1 was added to the activated carbon-added sample after being left sealed for 3 days as shown in Example 1 at 1% of the sample.
4% and 5% (total 10%) were added sequentially, and the odor components generated at that time were measured in the same manner as in Example 1.The measurements were carried out one hour after each addition. In addition, when adding 1% and 4%, the sample and activated carbon were mixed by stirring with a glass rod, but when adding 5%, the activated carbon was placed in a glass container. After charging, the container was sealed and the corner of the container was photographed for several minutes.The results are shown in Table 2.

第2表 以上の結果から明らかなとおり、生鮮廃棄物に対して、
1%の活性炭を添加すれば充分に臭気の発生を抑制する
効果が得られ、それ以上添加しても抑制効果は変らない
ことが判る。
As is clear from the results in Table 2 and above, for perishable waste,
It can be seen that the addition of 1% activated carbon sufficiently suppresses the odor generation, and that the suppressing effect does not change even if more is added.

なお、5%追加添加では、合計活性炭使用已は10%と
多いにも拘らず、トリメチルアミン、およびアンモニア
の濃度が上昇しているが、これは活性炭を添加後、ガラ
ス容器を強娠したため、生鮮廃棄物内に醸成した臭気成
分が一気に外部に洩出したためと考えられる。このこと
は、本発明の実際の適用に際して、生鮮廃棄物と活性炭
との強度の混合は却って不適当であることを示唆するも
のと言える。
In addition, when adding 5% additionally, the concentrations of trimethylamine and ammonia increased even though the total activated carbon usage was as high as 10%. This is thought to be due to the odor components that had built up in the waste leaking out all at once. This can be said to suggest that intensive mixing of perishable waste and activated carbon is rather inappropriate in the actual application of the present invention.

実施例3 試料として、臨海工場の取水口附近に繁殖したむらさき
貝を採取して用いた。これを200Clづつ4組に分け
、それぞれを2Qのガラス容器に装入すると共に、1組
を除いて、他の3組には、粉状活性炭2粒状活性炭酸い
は鉄粉を、第3表の添加条件の項に示す条件で添加混合
した。その後ガラス容器を密封し、11日間放置した。
Example 3 As a sample, purple mussels that grew near the water intake of a waterfront factory were collected and used. Divide this into 4 sets of 200Cl each and charge each set into a 2Q glass container. Except for 1 set, the other 3 sets are filled with powdered activated carbon, 2 granular activated carbon dioxide, or iron powder as shown in Table 3. They were added and mixed under the conditions shown in the addition conditions section. Thereafter, the glass container was sealed and left for 11 days.

なお、この時に用いた粉末活性炭は、実施例1で用いた
のと同じ活性炭であり、粒状活性炭はダイアソーブW1
0−30(三協産業株式会社製活性炭、商品名)であっ
て、その物性は以下のとおりである。
The powdered activated carbon used at this time was the same activated carbon used in Example 1, and the granular activated carbon was Diasorb W1.
0-30 (activated carbon manufactured by Sankyo Sangyo Co., Ltd., trade name), and its physical properties are as follows.

粒If 10〜32メツシユの範囲 96.0%水分 
             2.0%ml”7素吸着力
        1050mO/Clrメチレンブルー
脱色力     160mff/gr又、鉄粉について
は、通常市販の鉄粉を用いた。
Grain If Range of 10 to 32 mesh 96.0% moisture
2.0% ml"7 elemental adsorption power 1050 mO/Clr methylene blue decolorizing power 160 mff/gr As for the iron powder, commercially available iron powder was used.

前記密封試料を11日間常温(約20’C)で放置後、
ガラス容器内の気体を採取して、主な臭気成分の′a度
を測定した。測定方法は実施例1の場合と同様の方法に
よった。測定結果を第3表に示す。
After leaving the sealed sample at room temperature (approximately 20'C) for 11 days,
The gas in the glass container was sampled and the degree of 'a' of the main odor components was measured. The measurement method was the same as in Example 1. The measurement results are shown in Table 3.

第3表 この表から判るとおり、ケース1の活性炭無添加の場合
にあっては、各臭気成分ともかなりの高濃度であるの対
し、活性炭や鉄を予め添加混入しである場合には、活性
炭無添加の場合に比し、いずれの臭気成分も低濃度であ
るのが判る。特に注目すべきはケース2の鉄粉を用いた
場合、硫化水素は検出不能にまで低濃度に抑制されてい
ることである。又、ケース3は粉末炭を、ケーイ4は粒
状炭を添加し、粉末炭と粒状、炭の効果の差をみるため
に実施した試験の結果であるが両者を比較するに数値的
に大差はなく、粉末炭1粒状炭いずれについても臭気発
生抑制効果のあることが判る。
Table 3 As can be seen from this table, in case 1, in which activated carbon is not added, each odor component is at a fairly high concentration, whereas in case activated carbon and iron are added and mixed in advance, activated carbon It can be seen that the concentrations of all odor components are lower than in the case without additives. What is particularly noteworthy is that when iron powder in Case 2 is used, hydrogen sulfide is suppressed to a low concentration that is undetectable. In addition, case 3 added powdered charcoal, and Case 4 added granular charcoal. These are the results of a test conducted to see the difference in the effects of powdered charcoal, granular charcoal, and charcoal, but there is no numerically large difference when comparing the two. It can be seen that both powdered charcoal and granular charcoal have an odor generation suppressing effect.

実施例4 次に実施例3で用いたそれぞれの試料に対して、更に活
性炭を鉄粉を第4表の添加条件の項に示す条件で追加混
入し、ガラス容器を密封してから1時間経過後それぞれ
の臭気成分の濃度を測定した。
Example 4 Next, activated carbon and iron powder were added to each sample used in Example 3 under the conditions shown in the addition conditions section of Table 4, and the glass container was sealed for 1 hour. Afterwards, the concentration of each odor component was measured.

測定結果を第4表に示す。なお、ケースの番号は実施例
3の場合と対応させている。
The measurement results are shown in Table 4. Note that the case numbers correspond to those of the third embodiment.

第4表 この表から判るとおり、活性炭や、鉄の添加混入は、臭
気抑制に対して速効性があると共に、粉末炭1粒状炭、
鉄の王者を配合して用いれば(ケース2)、より効果が
大きいことが判る。
Table 4 As can be seen from this table, the addition of activated carbon and iron has a fast effect on odor control, as well as powdered charcoal, granular charcoal,
It can be seen that if Iron King is used in combination (Case 2), the effect is even greater.

[発明の効果1 本発明は以上のべたように、生鮮廃棄物から発生する悪
臭成分が活性炭に吸着され、その発散が抑制されるので
、ある程度の期間、野積み保管しても、悪臭公害を防止
できて、環境改善に役立つものである。
[Effect of the invention 1] As described above, the present invention allows malodor components generated from perishable waste to be adsorbed to activated carbon and suppresses its release, so even if stored in the open for a certain period of time, it will not cause malodor pollution. It is preventable and helps improve the environment.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は、本発明装置の一例の一部切欠側面図である。 1・・・受入れホッパー 2・・・生鮮廃棄物排出は構 3・・・活性炭ホッパー FIG. 1 is a partially cutaway side view of an example of the device of the present invention. 1...Accepting hopper 2...Discharge of perishable waste is a matter of concern. 3...Activated carbon hopper

Claims (1)

【特許請求の範囲】 1 生鮮廃棄物に活性炭を混入することを特徴とする生
鮮廃棄物から発生する臭気を抑制する方法。 2 活性炭が粉状活性炭および/または粒状活性炭であ
る特許請求の範囲第1項記載の生鮮廃棄物から発生する
臭気を抑制する方法。 3 活性炭が鉄の混入されたものである特許請求の範囲
第1項記載の生鮮廃棄物から発生する臭気を抑制する方
法。 4 生鮮廃棄物の投入される受入れホッパー、該受入れ
ホッパー底面開口部と接続する生鮮廃棄物排出機構、該
排出機構の途中に設けられる排出機構内を移動中の生鮮
廃棄物に活性炭を供給する活性炭ホッパー、および該ホ
ッパー底面開口部に設けられた活性炭の定量切出し装置
とを備え、前記排出機構内を移動中の生鮮廃棄物に活性
炭ホッパーから一定量の活性炭を混入して系外に排出す
るようにしたことを特徴とする生鮮廃棄物から発生する
臭気を抑制する装置。
[Claims] 1. A method for suppressing odors generated from perishable waste, which comprises mixing activated carbon into perishable waste. 2. The method for suppressing odors generated from fresh waste according to claim 1, wherein the activated carbon is powdered activated carbon and/or granular activated carbon. 3. A method for suppressing odors generated from fresh waste according to claim 1, wherein the activated carbon is mixed with iron. 4. A receiving hopper into which perishable waste is input, a perishable waste discharge mechanism connected to the bottom opening of the receiving hopper, and an activated carbon supplying activated carbon to the perishable waste moving within the discharge mechanism provided in the middle of the discharge mechanism. It is equipped with a hopper and an activated carbon quantitative cutting device provided at the bottom opening of the hopper, and is configured to mix a certain amount of activated carbon into the perishable waste moving within the discharge mechanism from the activated carbon hopper and discharge it out of the system. A device for suppressing odors generated from perishable waste, characterized by:
JP61302595A 1986-12-18 1986-12-18 Method and device for controlling development of rancidity from waste perishables Pending JPS63156585A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61302595A JPS63156585A (en) 1986-12-18 1986-12-18 Method and device for controlling development of rancidity from waste perishables

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61302595A JPS63156585A (en) 1986-12-18 1986-12-18 Method and device for controlling development of rancidity from waste perishables

Publications (1)

Publication Number Publication Date
JPS63156585A true JPS63156585A (en) 1988-06-29

Family

ID=17910869

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61302595A Pending JPS63156585A (en) 1986-12-18 1986-12-18 Method and device for controlling development of rancidity from waste perishables

Country Status (1)

Country Link
JP (1) JPS63156585A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7391192B2 (en) 2000-08-31 2008-06-24 Primarion, Inc. Apparatus and system for providing transient suppression power regulation

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7391192B2 (en) 2000-08-31 2008-06-24 Primarion, Inc. Apparatus and system for providing transient suppression power regulation
US7616456B2 (en) 2000-08-31 2009-11-10 Primarion Corporation Apparatus and system for providing transient suppression power regulation

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