JP3291739B2 - Filter material for fixing microorganisms for deodorization - Google Patents

Filter material for fixing microorganisms for deodorization

Info

Publication number
JP3291739B2
JP3291739B2 JP13757591A JP13757591A JP3291739B2 JP 3291739 B2 JP3291739 B2 JP 3291739B2 JP 13757591 A JP13757591 A JP 13757591A JP 13757591 A JP13757591 A JP 13757591A JP 3291739 B2 JP3291739 B2 JP 3291739B2
Authority
JP
Japan
Prior art keywords
lime
deodorization
microorganisms
neutralized
filter material
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
Application number
JP13757591A
Other languages
Japanese (ja)
Other versions
JPH04362074A (en
Inventor
正康 山崎
直人 北原
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.)
Mitsubishi Materials Corp
Original Assignee
Mitsubishi Materials Corp
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Filing date
Publication date
Application filed by Mitsubishi Materials Corp filed Critical Mitsubishi Materials Corp
Priority to JP13757591A priority Critical patent/JP3291739B2/en
Publication of JPH04362074A publication Critical patent/JPH04362074A/en
Application granted granted Critical
Publication of JP3291739B2 publication Critical patent/JP3291739B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/02Agglomerated materials, e.g. artificial aggregates
    • C04B18/021Agglomerated materials, e.g. artificial aggregates agglomerated by a mineral binder, e.g. cement
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B28/00Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
    • C04B28/18Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing mixtures of the silica-lime type
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/00017Aspects relating to the protection of the environment
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/00241Physical properties of the materials not provided for elsewhere in C04B2111/00
    • C04B2111/00267Materials permeable to vapours or gases
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/00474Uses not provided for elsewhere in C04B2111/00
    • C04B2111/00793Uses not provided for elsewhere in C04B2111/00 as filters or diaphragms

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Ceramic Engineering (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Organic Chemistry (AREA)
  • Civil Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
  • Treating Waste Gases (AREA)
  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (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】本発明は脱臭用微生物固定用フィ
ルタ材に係り、特に微生物脱臭方式による脱臭装置に充
填される脱臭フィルタ材料として有用な表層中和石灰系
多孔質硬化体よりなる脱臭用微生物固定用フィルタ材
関する。
The present invention relates to a filter for fixing microorganisms for deodorization.
More particularly, the present invention relates to a filter material for fixing microorganisms for deodorization, comprising a surface layer neutralized lime-based porous hardened material useful as a deodorization filter material to be filled in a deodorization apparatus employing a microorganism deodorization method.

【0002】[0002]

【従来の技術】土壌中の微生物等を利用した微生物脱臭
方式による脱臭装置は、無窓鶏舎等の家畜飼養施設から
発生する悪臭等の脱臭装置として既に実用化されてい
る。一般の微生物脱臭装置では、脱臭微生物固定用のフ
ィルタを充填した充填塔内に、循環水を散布しながら、
悪臭を有する気流を通気させることにより脱臭を行な
う。従来、このような脱臭装置に用いられる脱臭微生物
を固定化するためのフィルタとしては、樹脂製のものが
用いられていたが、比表面積が小さく装置が大型化す
る、表面が滑らかで微生物の固定に時間がかかる等の問
題点があった。そのため、近年では、セラミック繊維を
紙化した後、蜂の巣状のハニカム構造に成形したもの等
が用いられるようになった。
2. Description of the Related Art A deodorizing apparatus based on a microorganism deodorizing method utilizing microorganisms and the like in soil has already been put into practical use as a deodorizing apparatus for odors generated from livestock raising facilities such as windowless poultry houses. In a general microorganism deodorizer, while spraying circulating water into a packed tower filled with a filter for fixing deodorized microorganisms,
Deodorization is performed by aerating an odorous air flow. Conventionally, a filter made of resin has been used as a filter for immobilizing deodorizing microorganisms used in such a deodorizing apparatus. However, the specific surface area is small, the apparatus is large, and the surface is smooth and the microorganisms are immobilized. And it takes time. Therefore, in recent years, ceramic fibers formed into paper and then formed into a honeycomb-shaped honeycomb structure have been used.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、上記セ
ラミック繊維よりなるフィルタでは、セラミック繊維が
高価であることから処理コストの高騰を引き起こす、取
り扱い性に難があり、取り替えが困難である、使用済み
フィルタの処理が難しいといった欠点を有している。
However, in the filter made of the above-mentioned ceramic fiber, since the cost of the ceramic fiber is high, the processing cost rises, the handling property is difficult, and the used filter is difficult to replace. Has the drawback that processing is difficult.

【0004】本発明は上記従来の問題点を解決し、微生
物脱臭方式の脱臭装置で用いられる微生物固定用のフィ
ルタ材料として好適な脱臭用微生物固定用フィルタ材
提供することを目的とする。
An object of the present invention is to solve the above-mentioned conventional problems and to provide a filter material for fixing microorganisms for deodorization which is suitable as a filter material for fixing microorganisms used in a deodorizing apparatus of a microorganism deodorizing method.

【0005】[0005]

【課題を解決するための手段】本発明の脱臭用微生物固
定用フィルタ材は、CaOを含む多孔質硬化体であっ
て、その外表面及び気孔内表面の表層部のCaOはリン
酸で中和されている表層中和石灰系多孔質硬化体よりな
ことを特徴とする。
The microorganisms for deodorization according to the present invention are provided.
The filter material for use is a porous hardened material containing CaO, and the surface layer of CaO on the outer surface and the inner surface of the pores is made of a surface-neutralized lime-based porous hardened material neutralized with phosphoric acid.
Characterized in that that.

【0006】以下に本発明を詳細に説明する。本発明の
脱臭用微生物固定用フィルタ材を構成する表層中和石灰
系多孔質硬化体は、発泡軽量コンクリート、珪酸カルシ
ウムなどのCaOを含む多孔質硬化体の外表面及び気孔
内表面の表層部のCaOをリン酸で中和してなるもので
ある。石灰系多孔質硬化体としては、天然鉱物や発泡軽
量コンクリートの廃材を用いることもでき、そのCaO
含有量は10〜100重量%であることが好ましい。ま
た、石灰系多孔質硬化体はシリカやその他の物質を含有
していても良い。
Hereinafter, the present invention will be described in detail. Of the present invention
The surface neutralized lime-based porous hardened material constituting the filter material for fixing microorganisms for deodorization is a foamed lightweight concrete, and a surface hardened surface of the porous hardened material containing CaO such as calcium silicate and the surface layer of CaO are phosphorylated. It is obtained by neutralizing with an acid. As the lime-based porous hardened material, natural minerals and waste materials of foamed lightweight concrete can be used.
The content is preferably from 10 to 100% by weight. Further, the lime-based porous cured body may contain silica and other substances.

【0007】特に、天然の鉱物では、一般に、カリウ
ム、ホウ素、マンガン、鉄等の化合物が微量成分として
含有されているが、これらの成分は肥料として有効な成
分である。このため、本発明の表層中和石灰系多孔質硬
化体のフィルタとしての使用後には、これを肥料として
有効利用することができ、極めて有利である。また、シ
リカを含むものにおいても、珪酸肥料として有効に廃材
利用することが可能である。
In particular, natural minerals generally contain compounds such as potassium, boron, manganese, and iron as trace components, and these components are effective as fertilizers. Therefore, after the surface neutralized lime-based porous hardened body of the present invention is used as a filter, it can be effectively used as a fertilizer, which is extremely advantageous. In addition, waste materials containing silica can be effectively used as silicate fertilizers.

【0008】本発明において、表層中和石灰系多孔質硬
化体の粒径は1〜100mm程度であることが好まし
い。ただし、粒径10mm以下の場合には、ネット状の
袋に入れることにより、見掛け上の大きさを10mm以
上とする。この粒径が10mmよりも小さいと、該硬化
体を脱臭装置のフィルタ材として充填塔内に充填使用し
た際、塔内の圧力損失が大きくなる。また、気孔が破壊
されて微生物の生息が困難となる。
In the present invention, the particle size of the surface layer neutralized lime-based cured porous material is preferably about 1 to 100 mm. However, when the particle size is 10 mm or less, the apparent size is set to 10 mm or more by placing the particles in a net-like bag. When the particle size is smaller than 10 mm, when the cured product is used in a packed tower as a filter material for a deodorizer, the pressure loss in the tower becomes large. In addition, the pores are destroyed, making it difficult for microorganisms to inhabit.

【0009】逆に、該硬化体の粒径が100mmよりも
大きいと、循環水への悪臭成分の溶け込み量が低下し、
脱臭効果が低下する。また、取り扱いが困難となる上
に、使用済みのものの処理が難しくなる。
Conversely, if the particle size of the cured product is larger than 100 mm, the amount of the malodorous component dissolved in the circulating water decreases,
Deodorizing effect decreases. In addition, handling becomes difficult, and processing of used products becomes difficult.

【0010】表層中和石灰系多孔質硬化体の気孔率は、
10〜60%程度とするのが好ましい。この気孔率が1
0%よりも小さいと、微生物の生息が困難となると共
に、循環水への悪臭成分の溶け込み量が低下し、脱臭効
果が低下する。逆に、60%よりも大きいと、該硬化体
の強度が低下し、詰め替え作業中などに破壊するおそれ
がある。
The porosity of the surface-neutralized lime-based porous cured product is as follows:
It is preferred to be about 10 to 60%. This porosity is 1
If it is less than 0%, it becomes difficult for microorganisms to inhabit, and the amount of malodor components dissolved into the circulating water decreases, and the deodorizing effect decreases. On the other hand, if it is larger than 60%, the strength of the cured product is reduced, and the cured product may be broken during refilling work or the like.

【0011】また、本発明において、リン酸による中和
の程度は、中和前の多孔質硬化体に含有される全CaO
の5〜50%のCaOが中和されてカルシウムのリン酸
塩となる程度であることが好ましい。
In the present invention, the degree of neutralization with phosphoric acid depends on the total amount of CaO contained in the porous cured body before neutralization.
It is preferable that 5 to 50% of CaO is neutralized to form calcium phosphate.

【0012】このような表層中和石灰系多孔質硬化体を
製造するには、例えば、まず、珪石、生石灰(CaO)
及び/又は消石灰(Ca(OH))、並びにセメント
を適当量混合し、得られた混合物を、発泡剤を含む水に
加え、これを型枠に流し込んで養生することにより、石
灰系多孔質硬化体を製造する。なお、この養生に際して
は、一次養生後、高温高圧養生することが望ましい。得
られた多孔質硬化体を型枠から取り出して所定の粒度に
粉砕した後、温度20〜50℃、濃度20〜50重量%
程度のリン酸水溶液中に1〜10分程度浸漬する。勿
論、20重量%以下でも、50重量%以上でも可能であ
るが、低濃度では、浸漬時間を長くする必要があり、高
濃度では、溶液の粘性が高いため撹拌操作等が必要であ
る。これにより、多孔質硬化体の外表面及び気孔内表面
の表層部のCaOがリン酸塩となって中和される。中和
処理後、多孔質硬化体にリン酸が残っている場合には1
00℃以上で乾燥して本発明の脱臭用微生物固定用フィ
ルタ材を構成する表層中和石灰系多孔質硬化体を得る。
[0012] To manufacture such table layer neutralizing lime porous cured material, for example, firstly, silica, lime (CaO)
And / or slaked lime (Ca (OH) 2 ) and cement are mixed in an appropriate amount, and the resulting mixture is added to water containing a foaming agent, and the mixture is poured into a mold and cured to obtain a lime-based porous material. A cured product is manufactured. In this curing, it is desirable to perform high-temperature and high-pressure curing after primary curing. After taking out the obtained porous hardened body from the mold and pulverizing it to a predetermined particle size, the temperature is 20 to 50 ° C. and the concentration is 20 to 50% by weight.
It is immersed in a phosphoric acid aqueous solution for about 1 to 10 minutes. Of course, it is possible to use 20% by weight or less or 50% by weight or more. However, at a low concentration, it is necessary to lengthen the immersion time, and at a high concentration, a stirring operation or the like is required because the viscosity of the solution is high. As a result, CaO in the surface layer of the outer surface and the inner surface of the pores of the porous cured body becomes phosphate and is neutralized. After the neutralization treatment, if phosphoric acid remains in the porous cured product, 1
Dry at 00 ° C. or higher and remove the microorganism for fixing deodorant of the present invention.
A surface-neutralized lime-based porous hardened material constituting the ruther material is obtained.

【0013】なお、この中和処理において、用いるリン
酸水溶液の濃度や温度、浸漬時間等を適宜設定すること
により、中和の程度を容易に調節することができる。ま
た、この際のリン酸水溶液の濃度及び温度、浸漬時間、
乾燥温度等に応じて得られる表層中和石灰系多孔質硬化
体の表層部には、CaOの中和により、リン酸カルシウ
ム、リン酸一水素カルシウム、リン酸二水素カルシウ
ム、水酸化アパタイト等の1種以上が様々な割合で形成
される。
In this neutralization treatment, the degree of neutralization can be easily adjusted by appropriately setting the concentration, temperature, immersion time and the like of the phosphoric acid aqueous solution to be used. In this case, the concentration and temperature of the phosphoric acid aqueous solution, the immersion time,
The surface layer of the surface layer neutralized lime-based porous hardened material obtained according to the drying temperature, etc. is neutralized with CaO to form one of calcium phosphate, calcium monohydrogen phosphate, calcium dihydrogen phosphate, and hydroxyapatite. The above is formed in various ratios.

【0014】[0014]

【作用】本発明の脱臭用微生物固定用フィルタ材を構成
する表層中和石灰系多孔質硬化体は、軽量発泡コンクリ
ートの廃材を利用して製造することもでき、非常に安価
である。また、塊状又は粒状として供給されるため取り
扱い性に優れる。しかも、多孔体であるため、充填塔に
充填使用した際、圧力損失が小さい。
The filter material of the present invention for fixing microorganisms for deodorization is constituted.
The surface layer neutralized lime-based porous hardened body can be manufactured using waste material of lightweight foamed concrete, and is very inexpensive. In addition, since they are supplied as lumps or granules, they are excellent in handleability. Moreover, since it is a porous material, the pressure loss is small when used in a packed tower.

【0015】ところで、家畜飼養施設から発生する悪臭
成分の主成分はアンモニアである。このアンモニア脱臭
に関係する微生物の中には、アンモニアを亜硝酸、更に
は硝酸に変える好気性の亜硝酸菌及び硝酸菌と、亜硝酸
や硝酸を窒素に変える嫌気性の脱窒菌がある。一般のア
ンモニア脱臭の場合、一部のアンモニアを硝酸(亜硝酸
を含む)に変え、中和反応により脱臭する。しかしなが
ら、この方法では、循環水中の窒素濃度が高くなり、定
期的に循環水を入れ替える必要がある。これに対し、本
発明の脱臭用微生物固定用フィルタ材を構成する表層中
和石灰系多孔質硬化体では、循環水が常時入れ替わる表
層部に好気性の亜硝酸菌や硝酸菌が、内部の循環水の入
れ替わりがない部分に嫌気性の脱窒菌が生息する。この
ため、アンモニアを最終的に窒素にまで分解することが
でき、循環水中の窒素濃度を上げることなく、効率的に
脱臭処理することができる。
By the way, the main component of the offensive odor component generated from livestock raising facilities is ammonia. Among the microorganisms involved in this ammonia deodorization, there are aerobic nitrites and nitrates that convert ammonia to nitrite and further to nitrate, and anaerobic denitrifiers that convert nitrite and nitrate to nitrogen. In the case of general ammonia deodorization, a part of ammonia is changed to nitric acid (including nitrous acid) and deodorized by a neutralization reaction. However, in this method, the nitrogen concentration in the circulating water increases, and it is necessary to periodically change the circulating water. On the other hand, in the surface neutralized lime-based porous hardened material constituting the filter material for fixing microorganisms for deodorization of the present invention, aerobic nitrites and nitrates are circulated in the surface layer where circulating water is constantly replaced. Anaerobic denitrifying bacteria inhabit where water is not replaced. For this reason, ammonia can be finally decomposed to nitrogen, and the deodorizing treatment can be performed efficiently without increasing the nitrogen concentration in the circulating water.

【0016】また、微生物の栄養源として必要なもの
に、窒素とリンがある。アンモニア脱臭の場合、窒素は
アンモニアとして供給されるが、リンは供給されないた
め、他から供給する必要があるが、本発明の脱臭用微生
物固定用フィルタ材を構成する表層中和石灰系多孔質硬
化体では、表層部にリン分を含むため、別途供給する必
要がない。
Further, nitrogen and phosphorus are necessary as nutrient sources for microorganisms. In the case of ammonia deodorization, nitrogen is supplied as ammonia, but phosphorus is not supplied. Therefore, it is necessary to supply nitrogen from other sources.
In the surface-layer neutralized lime-based porous hardened material constituting the object-fixing filter material , the surface layer portion contains phosphorus, so that it is not necessary to separately supply it.

【0017】更に、本発明の脱臭用微生物固定用フィル
タ材を構成する表層中和石灰系多孔質硬化体では、表層
のCaOのカルシウムが不溶性のリン酸塩とされている
ため、CaOの溶出が殆どなく、脱臭装置の循環水のp
Hは、微生物の生育に適性なpH、即ちpH7程度の中
性とされる。このため、微生物は良好な生育環境に保持
される。因みに、表層部のCaOがリン酸塩とされてい
ない石灰系多孔質硬化体では、含有されるCaOが若干
ではあるが溶出するため、循環水はpH9〜10程度の
アルカリ性となり、微生物の生育に好ましくない。
Further, the microorganism-fixing film for deodorization of the present invention.
In the surface-neutralized lime-based porous hardened material constituting the raw material, since CaO in the surface layer is insoluble phosphate, CaO is hardly eluted and p of the circulating water of the deodorizer is reduced.
H is a neutral pH suitable for the growth of microorganisms, that is, about pH7. Therefore, the microorganisms are maintained in a favorable growth environment. By the way, in the lime-based porous hardened body in which CaO in the surface layer is not converted to phosphate, the CaO contained is slightly eluted, so that the circulating water becomes alkaline with a pH of about 9 to 10, and the growth of microorganisms is reduced. Not preferred.

【0018】なお、微生物脱臭方式の問題点として、装
置運転開始時の立ち上がりに時間がかかるという点が挙
げられるが、本発明の脱臭用微生物固定用フィルタ材を
構成する表層中和石灰系多孔質硬化体では、表層部のリ
ン酸塩により、次のような化学反応が起き、即時立ち上
げが可能である。即ち、表層部に含まれるリン酸塩Ca
HPOは悪臭成分のアンモニアを触媒としてCa10
(PO(OH)に変化し、この際、余剰のリン
酸を放出するが、この放出されたリン酸とアンモニアが
中和反応によりリン酸アンモニウムとして沈殿する。こ
れにより、アンモニアを除去することができる。
One of the problems of the microorganism deodorizing method is that it takes time to start the apparatus at the start of operation, but the filter material for fixing microorganisms for deodorizing of the present invention is not suitable.
In the surface layer neutralized lime-based porous hardened material constituting the surface layer portion, the following chemical reaction occurs due to the phosphate in the surface layer portion, and immediate start-up is possible. That is, the phosphate Ca contained in the surface layer portion
HPO 4 uses Ca 10 as a catalyst with ammonia as a malodorous component as a catalyst.
It changes to (PO 4 ) 6 (OH) 2 , which releases excess phosphoric acid. The released phosphoric acid and ammonia precipitate as ammonium phosphate by a neutralization reaction. Thereby, ammonia can be removed.

【0019】また、本発明の脱臭用微生物固定用フィル
タ材を構成する表層中和石灰系多孔質硬化体は、石灰系
であるため、フィルタ材料として使用後、土壌改良材と
して有効利用することができる。更に、本発明の脱臭用
微生物固定用フィルタ材を構成する表層中和石灰系多孔
質硬化体は、植物の生育に必要不可欠なリン酸塩を含む
ため、使用後、肥料として有効利用を図ることができ
る。更に、シリカを多く含む場合には、珪酸肥料とし
て、ホウ素、マンガン、鉄等の植物に必要な微量添加物
を含む場合にも肥料として極めて有効に利用できる。特
に、アンモニア脱臭に用いた場合には、カリウム分、リ
ン酸分に加えて、アンモニア体窒素及び微生物の作用に
より形成された硝酸体窒素を含むものとなり、植物に必
要な3大要素を総て含む良質な肥料となる。このような
ことから、本発明の脱臭用微生物固定用フィルタ材を構
成する表層中和石灰系多孔質硬化体は、使用後、土壌や
農耕地に散布することができ、廃棄物も有効に用いるこ
とができるといった利点を有する。
Further, the present invention provides a deodorizing microorganism-fixing film according to the present invention.
Since the surface layer neutralized lime-based porous hardened material constituting the tar material is lime-based, it can be effectively used as a soil improving material after being used as a filter material. Furthermore, for the deodorization of the present invention
Since the surface layer neutralized lime-based porous hardened material constituting the filter material for fixing microorganisms contains a phosphate indispensable for the growth of plants, it can be effectively used as a fertilizer after use. Furthermore, when a large amount of silica is contained, it can be used very effectively as a silicate fertilizer as a fertilizer even when it contains a small amount of additives required for plants such as boron, manganese, and iron. In particular, when used for ammonia deodorization, it contains ammonia nitrogen and nitrate nitrogen formed by the action of microorganisms in addition to potassium and phosphoric acid, and all three major elements necessary for plants are included. It will be a good quality fertilizer including. Therefore , the filter material for fixing microorganisms for deodorization of the present invention is constituted.
The resulting surface neutralized lime-based porous hardened body has the advantage that after use, it can be sprayed on soil or agricultural land, and waste can be used effectively.

【0020】[0020]

【実施例】以下に実施例及び比較例を挙げて本発明をよ
り具体的に説明する。
The present invention will be described more specifically below with reference to examples and comparative examples.

【0021】実施例1、比較例1〜3 表1に示すフィルタ材料を微生物脱臭方式のアンモニア
脱臭装置の充填塔に充填し、無窓鶏舎からの排気の脱臭
処理を行ない、結果を表1に示した。
Example 1, Comparative Examples 1 to 3 The filter materials shown in Table 1 were packed in a packed tower of an ammonia deodorizing apparatus of a microbial deodorizing system, and the exhaust air from the windowless poultry house was deodorized. The results are shown in Table 1. Was.

【0022】なお、比較例3で用いた石灰系多孔質硬化
体及び実施例1で用いた表層中和石灰系多孔質硬化体
は、次のようにして製造した。
The lime-based porous hardened material used in Comparative Example 3 and the surface layer neutralized lime-based porous hardened material used in Example 1 were produced as follows.

【0023】粉末の珪石、CaO、セメントを重量比
3:1:1の割合で混合し、発泡剤0.1重量%を含む
水溶液中に添加混合した。これを型枠に流し込み、25
℃で2時間一次養生した後、10atm、180℃で1
6時間高温高圧(オートクレーブ)養生して発泡させ
た。得られた硬化体を型枠から取り出して粉砕し、石灰
系多孔質硬化体とした。このものの粒径は50〜80m
m、気孔率は42%であった。
The powdered silica, CaO, and cement were mixed at a weight ratio of 3: 1: 1, and added to and mixed with an aqueous solution containing 0.1% by weight of a foaming agent. Pour this into the formwork, 25
After primary curing at 2 ℃ for 2 hours, 10atm, 1 at 180 ℃
The foam was cured by heating at a high temperature and a high pressure (autoclave) for 6 hours. The obtained cured product was taken out of the mold and pulverized to obtain a lime-based porous cured product. The particle size of this is 50-80m
m and porosity was 42%.

【0024】また、上記石灰系多孔質硬化体を25℃の
20重量%リン酸水溶液に2分浸漬して中和処理した
後、100℃で20時間乾燥した。得られた表層中和石
灰系多孔質硬化体は、蛍光X線分析により調べたとこ
ろ、中和処理前の石灰系多孔質硬化体の全CaOの22
重量%のCaOがリン酸塩に中和されたものであり、表
層部のカルシウムは殆どがリン酸一水素カルシウムで、
一部がリン酸カルシウム及び水酸化アパタイトの形態と
なっていた。
The cured lime-based porous material was immersed in a 20% by weight aqueous solution of phosphoric acid at 25 ° C. for 2 minutes for neutralization, and then dried at 100 ° C. for 20 hours. The obtained surface layer neutralized lime-based porous hardened product was examined by X-ray fluorescence analysis. As a result, 22% of the total CaO of the lime-based porous hardened product before the neutralization treatment was obtained.
Weight% of CaO is neutralized to phosphate, and the surface calcium is mostly calcium monohydrogen phosphate,
Some were in the form of calcium phosphate and hydroxyapatite.

【0025】[0025]

【表1】 [Table 1]

【0026】表1より次のことが明らかである。即ち、
従来の樹脂製フィルタ材(比較例1)やセラミックスハ
ニカム構造体(比較例2)を用いた場合には、アンモニ
アの除去効率が悪く、全窒素が循環水中に蓄積する傾向
がある。
The following is clear from Table 1. That is,
When a conventional resin filter material (Comparative Example 1) or a ceramic honeycomb structure (Comparative Example 2) is used, the efficiency of removing ammonia is poor, and total nitrogen tends to accumulate in circulating water.

【0027】石灰系多孔質硬化体(比較例3)を用いた
場合には、循環水中の窒素濃度は比較的低いが、アンモ
ニアの除去効率が若干劣り、循環水のpHもアルカリ域
に経時変化する傾向を示す。
When the lime-based porous hardened material (Comparative Example 3) was used, the nitrogen concentration in the circulating water was relatively low, but the ammonia removal efficiency was slightly inferior, and the pH of the circulating water changed over time to an alkaline range. Show a tendency to.

【0028】これに対して、表層中和石灰系多孔質硬化
よりなる本発明の脱臭用微生物固定用フィルタ材(実
施例1)を用いた場合には、アンモニアの除去効率が著
しく高い。また、循環水中の全窒素濃度も低い上に循環
水のpH値も良好となる。
[0028] On the contrary, in the case of using Table layer neutralized lime porous deodorizing microorganism fixing the filter material of the cured body from the consisting invention (Example 1) is significantly higher ammonia removal efficiency. In addition, the total nitrogen concentration in the circulating water is low, and the pH value of the circulating water is good.

【0029】[0029]

【発明の効果】以上詳述した通り、本発明の脱臭用微生
物固定用フィルタ材によれば 微生物の生息に好適
な中性を示す。 塊状又は粒状とすることができ、取
り扱い性に優れる。 多孔質体であるため、充填塔に
使用した際、圧力損失が小さい。 安価に提供され
る。 使用後、肥料、土壌改質材等として有効利用を
図れる。 好気性及び嫌気性菌の両微生物を生息させ
ることができ、これによりアンモニアを窒素にまで分解
して良好な処理を行なえる。等の優れた効果が奏され、
その工業的有用性は極めて大である。
As described in detail above, the deodorizing microorganism of the present invention is used.
According to the filter material for fixing objects, the material exhibits neutrality suitable for the inhabitation of microorganisms. It can be made into a lump or a granule, and is excellent in handleability. Since it is a porous body, it has a small pressure loss when used in a packed tower. Provided at low cost. After use, it can be effectively used as fertilizer, soil modifying material, etc. Both aerobic and anaerobic microorganisms can be inhabited, whereby ammonia can be decomposed to nitrogen and good treatment can be performed. Excellent effects such as
Its industrial utility is extremely large.

───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) C04B 41/00 - 41/72 ──────────────────────────────────────────────────続 き Continued on front page (58) Field surveyed (Int. Cl. 7 , DB name) C04B 41/00-41/72

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 CaOを含む多孔質硬化体であって、そ
の外表面及び気孔内表面の表層部のCaOはリン酸で中
和されている表層中和石灰系多孔質硬化体よりなること
を特徴とする脱臭用微生物固定用フィルタ材
1. A porous cured material containing CaO, that CaO of the surface layer portion of the outer surface and pore inner surfaces are made of Table layer neutralized lime porous cured material that has been neutralized with phosphoric acid
A filter material for fixing microorganisms for deodorization, comprising:
JP13757591A 1991-06-10 1991-06-10 Filter material for fixing microorganisms for deodorization Expired - Fee Related JP3291739B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP13757591A JP3291739B2 (en) 1991-06-10 1991-06-10 Filter material for fixing microorganisms for deodorization

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP13757591A JP3291739B2 (en) 1991-06-10 1991-06-10 Filter material for fixing microorganisms for deodorization

Publications (2)

Publication Number Publication Date
JPH04362074A JPH04362074A (en) 1992-12-15
JP3291739B2 true JP3291739B2 (en) 2002-06-10

Family

ID=15201928

Family Applications (1)

Application Number Title Priority Date Filing Date
JP13757591A Expired - Fee Related JP3291739B2 (en) 1991-06-10 1991-06-10 Filter material for fixing microorganisms for deodorization

Country Status (1)

Country Link
JP (1) JP3291739B2 (en)

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63267421A (en) * 1987-04-27 1988-11-04 Ebara Infilco Co Ltd Method for removing nitrogen oxide out of gas
JPH02237639A (en) * 1989-03-08 1990-09-20 Rasa Kogyo Kk Adsorbent

Also Published As

Publication number Publication date
JPH04362074A (en) 1992-12-15

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