JP2003137680A - Method of decreasing malodor in preparation of compost - Google Patents

Method of decreasing malodor in preparation of compost

Info

Publication number
JP2003137680A
JP2003137680A JP2001338012A JP2001338012A JP2003137680A JP 2003137680 A JP2003137680 A JP 2003137680A JP 2001338012 A JP2001338012 A JP 2001338012A JP 2001338012 A JP2001338012 A JP 2001338012A JP 2003137680 A JP2003137680 A JP 2003137680A
Authority
JP
Japan
Prior art keywords
compost
preparation
decreasing
nitrifying bacteria
bacteria
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
JP2001338012A
Other languages
Japanese (ja)
Inventor
Satoshi Tamaki
聡史 玉木
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.)
Sekisui Chemical Co Ltd
Original Assignee
Sekisui Chemical 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 Sekisui Chemical Co Ltd filed Critical Sekisui Chemical Co Ltd
Priority to JP2001338012A priority Critical patent/JP2003137680A/en
Publication of JP2003137680A publication Critical patent/JP2003137680A/en
Pending legal-status Critical Current

Links

Classifications

    • 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

Landscapes

  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)
  • Fertilizers (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method of inexpensively and easily decreasing the malodors produced in preparing compost which is applicable even to a motor driven garbage disposal machine for household use. SOLUTION: This method of decreasing the malodors produced in preparing the compost comprises adding autotrophic nitrifying bacteria to the material to be prepared as the compost, thereby decreasing the ammonia odors generated from the material to be prepared as the compost in preparing the compost from organic wastes.

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、有機性廃棄物をコ
ンポスト調製する際に発生する悪臭を低減する方法に関
する。
TECHNICAL FIELD The present invention relates to a method for reducing the malodor generated when composting organic waste.

【0002】[0002]

【従来の技術】家庭内などで発生する生ごみを、コンポ
スト化して利用することは、資源の再利用とごみ処理対
策の一環として注目されている。しかしながら、前記コ
ンポスト調製時に発生する臭気は、近年普及の著しい家
庭用電動生ゴミ処理機で特に問題となっている。この臭
気を低減化するため、これまで触媒と電熱ヒーターを利
用したり、吸着剤による脱臭装置を付加する方法が提案
されている(例えば、特開平5−221767号公
報)。しかしながら、これらの装置は、初期コストやラ
ンニングコストを高価にするだけでなく、想定した量を
超える臭気発生に対応出来ないという問題点があった。
2. Description of the Related Art The composting and utilization of food waste generated at home has attracted attention as a part of resource reuse and garbage disposal measures. However, the odor generated during the preparation of the compost has been a serious problem in electric household garbage disposal machines for household use, which have become very popular in recent years. In order to reduce this odor, there has been proposed a method of utilizing a catalyst and an electric heater or adding a deodorizing device using an adsorbent (for example, JP-A-5-221767). However, these devices not only increase the initial cost and running cost, but also have a problem that they cannot cope with the generation of odors exceeding the expected amount.

【0003】これに対して、コンポスト化の過程におい
て発生する悪臭物質に注目し、その主要物質であるアン
モニアを微生物による硝化反応を利用して脱臭する生物
脱臭装置も研究され実用化が試みられている。しかしな
がら、これら方法は、まだ家庭用電動生ゴミ処理機に応
用するという点では、維持管理や初期コストの問題から
困難であった。
On the other hand, attention has been paid to the malodorous substances generated in the process of composting, and a biological deodorizing device for deodorizing the main substance, ammonia, by utilizing the nitrification reaction by microorganisms has also been studied and attempted to be put into practical use. There is. However, these methods are still difficult in terms of maintenance and initial cost in that they are applied to electric household garbage disposers for home use.

【0004】[0004]

【発明が解決しようとする課題】本発明は上記問題点に
鑑み、家庭用電動ゴミ処理機にも応用出来る安価で簡易
的に、コンポスト調製時に発生する悪臭を低減する方法
を提供することを目的とする。
In view of the above problems, it is an object of the present invention to provide a method for reducing the malodor generated during compost preparation, which can be applied to an electric household waste disposal machine and is inexpensive and simple. And

【0005】[0005]

【課題を解決するための手段】本発明は、有機性廃棄物
をコンポスト調製する際に、コンポスト調製物に独立栄
養性硝化菌を添加することによりコンポスト調製物から
発生するアンモニア臭を低減させることを特徴とするコ
ンポスト調製時の悪臭低減化方法である。
The present invention reduces the ammonia odor generated from a compost preparation by adding autotrophic nitrifying bacteria to the compost preparation when composting an organic waste. Is a method of reducing malodor during compost preparation.

【0006】上記有機性廃棄物とは例えば、家庭や事業
所で排出される生ごみ;食品加工場で排出される動植物
性残渣;廃水処理場で生成する余剰汚泥;畜産場で排出
される家畜糞尿;農家で排出される稲藁;籾殻など、主
として生分解性の有機物からなる廃棄物のことを意味す
る。
[0006] The above-mentioned organic wastes include, for example, food waste discharged from homes and businesses; animal and plant residues discharged from food processing plants; surplus sludge generated from wastewater treatment plants; livestock discharged from livestock farms. Manure; rice straw discharged by farmers; rice husks and other wastes mainly composed of biodegradable organic matter.

【0007】上記コンポストとは、有機性廃棄物が堆肥
化されたものを意味する。また、本発明で言うコンポス
ト調製物とは、有機性廃棄物がコンポストへと処理され
る際の中間物のことを意味する。すなわち、有機性廃棄
物と生じるコンポストとの混合物全体のことである。
The above-mentioned compost means a composted organic waste. In addition, the compost preparation according to the present invention means an intermediate when the organic waste is processed into compost. That is, the entire mixture of organic waste and the resulting compost.

【0008】上記堆肥化の例として、自然を利用する方
法としては、畜舎敷料あるいは稲藁等に、し尿や台所排
水等を降りかけて積んで置き、時々上下を積み替えるこ
と(切返し)により酸素を供給して易分解性の有機物を
自然環境中の微生物で分解させる方法が挙げられる。ま
た、人工的には、人口容器に生ごみを投入した後、攪拌
翼および攪拌用モーターを付け、タイマーで一定時間毎
に自動的に攪拌することにより酸素供給下で易分解性有
機物を微生物により分解させる家庭用電動生ごみ処理機
の普及が進んでいる。
[0008] As an example of the above-mentioned composting, as a method of utilizing nature, oxygen is obtained by placing human dwelling bedding, rice straw, etc. on which night soil, kitchen drainage, etc. are dropped and piled up and down, and by occasionally transposing (cut back). A method of supplying easily, and decomposing easily decomposable organic matter with microorganisms in the natural environment can be mentioned. Also, artificially, after putting garbage into an artificial container, attach a stirring blade and a stirring motor, and automatically stir at regular intervals with a timer to easily decompose easily degradable organic matter by microorganisms under oxygen supply. Household electric garbage processing machines for disassembling are becoming popular.

【0009】本発明には、アルスロバクターグロビフォ
ーミス(Arthrobacterglobiform
is)のような従属栄養性硝化菌でなく独立栄養性硝化
菌を用いる。上記従属栄養性硝化菌は効率的に培養する
ことが困難である。それに対して独立栄養性硝化菌は、
比較的簡便な方法で培養することが可能であるので安価
に大量の菌を入手することが出来る。又、他の栄養源を
必要としないので、アンモニアだけを栄養価として迅速
に硝化反応を行えるからである。
The present invention includes Arthrobacter globiformis.
Not autotrophic nitrifying bacteria such as is) but autotrophic nitrifying bacteria are used. It is difficult to efficiently culture the above heterotrophic nitrifying bacteria. In contrast, autotrophic nitrifying bacteria are
Since it can be cultured by a relatively simple method, a large amount of bacteria can be obtained at low cost. Moreover, since no other nutrient source is required, nitrification reaction can be carried out rapidly with only ammonia as the nutritional value.

【0010】上記独立栄養性硝化菌としては、一般的に
知られるニトロソモナス(Nitrosomonas)
属、ニトロコッカス(Nitrococcus)属等、
一般に知られる硝化反応を行う菌が挙げられ、これらは
単独又は混合状態で用いられる。
The above-mentioned autotrophic nitrifying bacteria are generally known as Nitrosomonas.
Genus, Nitrococcus genus, etc.
Commonly known bacteria that perform a nitrification reaction can be mentioned, and these can be used alone or in a mixed state.

【0011】上記独立栄養性硝化菌の培養方法として
は、森林腐葉土と水を混合攪拌して、種々の菌を抽出し
た後、栄養源として炭酸アンモニウム等の無機アンモニ
ウム塩を加えて液体培養を行う方法;廃水処理設備の硝
化槽の処理液に栄養源として無機アンモニウム塩を加え
て液体培養を行う方法;培養液に硝化菌を付着させるた
めの担体を入れ、培養を継続して菌を担体に付着する方
法等が挙げられる。上記担体の種類は特に制限は無く、
既知の微生物による処理反応、処理槽等で使用されるも
のが用いられる。
As a method for culturing the above-mentioned autotrophic nitrifying bacteria, forest mulch and water are mixed and stirred to extract various bacteria, and then an inorganic ammonium salt such as ammonium carbonate is added as a nutrient source to perform liquid culture. Method: A method of performing liquid culture by adding an inorganic ammonium salt as a nutrient source to a treatment liquid in a nitrification tank of a wastewater treatment facility; a carrier for adhering nitrifying bacteria to the culture liquid is added, and the culture is continued to use the bacteria as a carrier. Examples of the method of attachment include the method. The type of the carrier is not particularly limited,
What is used in a treatment reaction by a known microorganism, a treatment tank or the like is used.

【0012】培養量は、例えば1日1kgの生ごみを処
理する家庭用電動生ごみ処理機の場合、硝化能力として
窒素負荷1g−N/day、好ましくは5g−N/da
y以上が好ましい。この能力以下の場合、本発明の効果
が得られない場合がある。その他の場合、1日当たりの
有機性廃棄物処理量に準じて上記の硝化能力を加減する
か、あるいは1日あたりの窒素負荷量を実測して、その
負荷量の20%以上の硝化能力となるまで培養すること
が好ましい。
The culture amount is, for example, in the case of a household electric food waste processing machine for processing 1 kg of food waste per day, the nitrogen load is 1 g-N / day, preferably 5 g-N / da as nitrification capacity.
y or more is preferable. If the capacity is less than this, the effect of the present invention may not be obtained. In other cases, the nitrification capacity is adjusted according to the amount of treated organic waste per day, or the nitrogen load per day is measured, and the nitrification capacity is 20% or more of the load. It is preferable to culture until.

【0013】上記の例で述べた液体培養法では通常、培
養液量が数Lから数十Lになる。これをそのまま処理槽
に投入すると、処理槽内のコンポストの含水率が大幅に
上昇し、コンポストの調製が困難となる。そのため50
ml程度まで濃縮するのが良い。濃縮方法の例として
は、遠心機による集菌など微生物学分野で一般的に使用
される方法が挙げられる。
In the liquid culture method described in the above example, the amount of culture liquid is usually several L to several tens L. If this is put into the treatment tank as it is, the water content of the compost in the treatment tank increases significantly, and it becomes difficult to prepare the compost. Therefore 50
It is better to concentrate to about ml. Examples of the concentration method include methods generally used in the field of microbiology, such as collecting cells by a centrifuge.

【0014】培養された菌は、培養液、上記濃縮物、担
体表面に菌を培養・付着させた菌付着担体等の形態で処
理槽内のコンポスト調製物に添加する事が出来る。菌を
加える時期は特に限定されないが例えば、コンポスト調
製を開始する時点、調製中のコンポストからアンモニア
臭が発生し始めた時点等が好ましい。
The cultivated bacteria can be added to the compost preparation in the treatment tank in the form of a culture solution, the above-mentioned concentrate, a bacterium-adhering carrier in which the bacterium is cultivated and adhered to the carrier surface. The timing of adding the bacterium is not particularly limited, but is preferably, for example, the time when the compost preparation is started, the time when the ammonia odor starts to be generated from the compost being prepared, or the like.

【0015】上記独立栄養性硝化菌をコンポスト調製物
に添加する際、上記独立栄養性硝化菌以外にも、メルカ
プタン類の他の悪臭物質を脱臭する菌や、有機物を分解
消化する菌等を併用しても良い。
When the above-mentioned autotrophic nitrifying bacteria are added to compost preparations, in addition to the above autotrophic nitrifying bacteria, bacteria that deodorize other malodorous substances such as mercaptans and bacteria that decompose and digest organic substances are also used. You may.

【0016】本発明において、上記コンポスト調製物の
内容として、外部から新たに有機性廃棄物を加える場合
には、既に生成しているコンポストの重量と新たな有機
性廃棄物の重量比を3:1以上にすることが好ましい。
さらに好ましくは、10:1以上である。3:1より低
い場合には、アンモニア臭の低減効果が十分に発揮され
ない場合や、多量のダニやカビが発生しコンポスト調製
がうまく行かない場合がある。尚、上記重量比は、水分
を含んだ湿潤状態での重量比である。
In the present invention, when the organic waste is newly added from the outside as the content of the above-mentioned compost preparation, the weight ratio of the already-produced compost to the weight of the new organic waste is 3: It is preferably 1 or more.
More preferably, it is 10: 1 or more. If the ratio is lower than 3: 1, the effect of reducing the ammonia odor may not be sufficiently exerted, or a large amount of mites and molds may be generated to make the compost preparation unsuccessful. The above weight ratio is a weight ratio in a wet state containing water.

【0017】また、コンポスト調製時の際、コンポスト
調製物の温度は、独立栄養性硝化菌の活性を長期間維持
するために10〜40℃に保つことが好ましい。より好
ましくは、20〜30℃である。
During the preparation of compost, the temperature of the compost preparation is preferably maintained at 10 to 40 ° C. in order to maintain the activity of autotrophic nitrifying bacteria for a long period of time. More preferably, it is 20 to 30 ° C.

【0018】上記温度調節する方法としては、生ごみ処
理装置等を使用する場合は、ヒーターや冷却装置を付け
る方法があるが、簡便には装置設計の段階でコンポスト
の重量と処理される有機性廃棄物の重量比を10:1程
度にすれば、微生物による発酵熱により自然に適度な温
度を保つことが出来る。
As a method for adjusting the temperature, when using a food waste treating device or the like, there is a method of attaching a heater or a cooling device, but simply, the weight of the compost and the organic material to be treated are added at the stage of designing the device. By setting the weight ratio of the waste to about 10: 1, it is possible to naturally maintain an appropriate temperature by the heat of fermentation by the microorganisms.

【0019】上記コンポスト調製物のpH値は、独立栄
養性硝化菌の活性を長期間維持するために6〜9の範囲
にすることが好ましい。より好ましくは、7.0〜8.
5の範囲である。上記pH範囲外では硝化菌の活性が低
下しアンモニア抑制効果が低下する。上記pHの調節方
法としては、有機性廃棄物の投入量を調節する手段が挙
げられる。
The pH value of the above compost preparation is preferably in the range of 6 to 9 in order to maintain the activity of autotrophic nitrifying bacteria for a long period of time. More preferably, it is 7.0 to 8.
The range is 5. Outside the above pH range, the activity of nitrifying bacteria is reduced and the ammonia suppressing effect is reduced. Examples of the method for adjusting the pH include means for adjusting the amount of organic waste input.

【0020】本発明の方法を実施する場所としては特に
限定されないが、通常使用される醗酵槽など、人工タン
ク内で行われる方が好ましい。
The place for carrying out the method of the present invention is not particularly limited, but it is preferably carried out in an artificial tank such as a commonly used fermenter.

【0021】また、コンポスト調製する際には、コンポ
スト化を効率的に進行させるために有機性廃棄物中の水
分を吸収する吸水材料を使用する方が好ましい。そのよ
うな吸水材料として、おが屑、吸水性ポリマー等が挙げ
られる。
Further, when preparing compost, it is preferable to use a water absorbing material that absorbs water in the organic waste in order to efficiently progress composting. Examples of such a water absorbing material include sawdust and water absorbing polymers.

【0022】[0022]

【発明の実施の形態】(実施例)市販の家庭用電動生ゴ
ミ処理機(槽容量45L)に、微生物源として腐葉土3
0L(約15kg)を詰め、有機性廃棄物として市販の
ドッグフードを1日1kg投入してコンポスト調製を行
った。このコンポスト調製物から発生するアンモニアガ
ス濃度を検知管法で毎日測定した。その結果、15日目
からアンモニアガスが発生した。そのアンモニアガス発
生濃度を測定した結果、2ppmであった。そこで予め
培養しておいた独立栄養性硝化菌50mlを上記コンポ
スト調製物に注入した。上記菌の投入後も、ドッグフー
ドを1日1kgづつ投入し、これを30日間継続した。
その後、コンポスト調製物から発生するアンモニアガス
濃度を測定した結果、4ppmであった。
BEST MODE FOR CARRYING OUT THE INVENTION (Example) In a commercially available household electric garbage processing machine (tank capacity: 45 L), humus 3 as a microbial source was used.
0 L (about 15 kg) was packed, and 1 kg of commercially available dog food was added as organic waste per day to prepare compost. The ammonia gas concentration generated from this compost preparation was measured daily by the detector tube method. As a result, ammonia gas was generated from the 15th day. As a result of measuring the ammonia gas generation concentration, it was 2 ppm. Therefore, 50 ml of autotrophic nitrifying bacteria that had been cultured in advance was injected into the above compost preparation. Even after the addition of the above bacteria, 1 kg of dog food was added per day, which was continued for 30 days.
Then, the concentration of ammonia gas generated from the compost preparation was measured and found to be 4 ppm.

【0023】(比較例)上記実施例において、15日目
にアンモニアガスが発生した時点で独立栄養性硝化菌を
上記コンポスト調製物に注入しなかったこと以外は同様
に行った。その結果、実施例と同じ最終測定時期にアン
モニアガス濃度を測定した結果、50ppmであった。
Comparative Example The same procedure as in the above Example was performed except that autotrophic nitrifying bacteria were not injected into the compost preparation at the time when ammonia gas was generated on the 15th day. As a result, the ammonia gas concentration was measured at the same final measurement time as in the example, and as a result, it was 50 ppm.

【0024】尚、上記に使用した独立栄養性硝化菌の培
養は以下の手順で行った。市販の腐葉土(30L)に水
道水25Lを添加後、攪拌し、腐葉土から各種の菌を抽
出した。抽出液に炭酸アンモニウム水溶液を添加し、独
立栄養硝化菌を培養した。培養は、培養液の硝酸濃度を
適宜測定し、硝酸濃度が4g−N03/Lになると培養
液を半量交換した。これを約8ヶ月間継続し、最終的な
硝化速度は、60g−N03/dayとなった。この培
養液を遠心機で濃縮し、最終的に50mlの濃縮培養液
を得た。
The autotrophic nitrifying bacteria used above were cultivated by the following procedure. After adding 25 L of tap water to commercially available mulch (30 L), the mixture was stirred and various fungi were extracted from the mulch. Aqueous ammonium carbonate solution was added to the extract to culture autotrophic nitrifying bacteria. For the culture, the nitric acid concentration of the culture solution was appropriately measured, and when the nitric acid concentration reached 4 g-N03 / L, the culture solution was exchanged by half. This was continued for about 8 months, and the final nitrification rate was 60 g-N03 / day. This culture solution was concentrated with a centrifuge to finally obtain 50 ml of a concentrated culture solution.

【0025】[0025]

【発明の効果】本発明の方法によると硝化菌の利用とい
う省エネルギーで簡便かつ、環境負荷の極めて少ない方
法で、コンポスト調製時におけるアンモニアの発生を低
減することが出来た。このことは、家庭用電動生ゴミ処
理機から発生する悪臭を低減させるという問題を解決す
る可能性があり、その普及に役立つと考えられる。
EFFECTS OF THE INVENTION According to the method of the present invention, it is possible to reduce the generation of ammonia during the preparation of compost by a method of utilizing nitrifying bacteria, which is energy-saving, simple, and has a very low environmental load. This may solve the problem of reducing the offensive odor generated from the electric household garbage disposer for home use, and is considered to be useful for its widespread use.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C12N 1/20 B09B 3/00 ZABA D Fターム(参考) 4B065 AA01X BB40 BC31 BD22 CA49 CA56 4D004 AA02 AA03 AA04 AC01 BA04 CA15 CA19 CA48 CB06 CB26 CC07 CC08 DA03 DA20 4D059 AA01 AA05 AA07 AA08 BA01 BA22 BA27 CA16 CC01 EB05 4H061 AA02 CC36 CC42 CC51 CC55 EE66 HH42 LL22 ─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification code FI theme code (reference) C12N 1/20 B09B 3/00 ZABA DF term (reference) 4B065 AA01X BB40 BC31 BD22 CA49 CA56 4D004 AA02 AA03 AA04 AC01 BA04 CA15 CA19 CA48 CB06 CB26 CC07 CC08 DA03 DA20 4D059 AA01 AA05 AA07 AA08 BA01 BA22 BA27 CA16 CC01 EB05 4H061 AA02 CC36 CC42 CC51 CC55 EE66 HH42 LL22

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】有機性廃棄物をコンポスト調製する際に、
コンポスト調製物に独立栄養性硝化菌を添加することに
より前記コンポスト調製物から発生するアンモニア臭を
低減することを特徴とするコンポスト調製時の悪臭低減
化方法。
1. When composting an organic waste,
A method for reducing malodor during compost preparation, which comprises reducing autonomic odor generated from the compost preparation by adding autotrophic nitrifying bacteria to the compost preparation.
【請求項2】コンポスト調製物のpH値を、6〜9の範
囲とする請求項1記載のコンポスト調製時の悪臭を低減
化する方法。
2. The method for reducing malodor during compost preparation according to claim 1, wherein the pH value of the compost preparation is in the range of 6-9.
JP2001338012A 2001-11-02 2001-11-02 Method of decreasing malodor in preparation of compost Pending JP2003137680A (en)

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Country Link
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010533572A (en) * 2007-08-08 2010-10-28 彭光浩 Method for removing carbon and nitrogen contaminants in contaminated water using heterotrophic ammonia oxidizing bacteria

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010533572A (en) * 2007-08-08 2010-10-28 彭光浩 Method for removing carbon and nitrogen contaminants in contaminated water using heterotrophic ammonia oxidizing bacteria

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