JPH07185318A - Deodorant material and its deodorizing and fertilizer making method - Google Patents

Deodorant material and its deodorizing and fertilizer making method

Info

Publication number
JPH07185318A
JPH07185318A JP35098193A JP35098193A JPH07185318A JP H07185318 A JPH07185318 A JP H07185318A JP 35098193 A JP35098193 A JP 35098193A JP 35098193 A JP35098193 A JP 35098193A JP H07185318 A JPH07185318 A JP H07185318A
Authority
JP
Japan
Prior art keywords
magnesium
compd
deodorizing
compound
deodorizing 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.)
Pending
Application number
JP35098193A
Other languages
Japanese (ja)
Inventor
Kikuo Kishimoto
菊夫 岸本
Kazuo Fukase
和男 深瀬
Kyoichi Kitsugi
恭一 木次
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.)
NAISU TEC KK
Original Assignee
NAISU TEC KK
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 NAISU TEC KK filed Critical NAISU TEC KK
Priority to JP35098193A priority Critical patent/JPH07185318A/en
Publication of JPH07185318A publication Critical patent/JPH07185318A/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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • 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

  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Fertilizers (AREA)
  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
  • Treating Waste Gases (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

PURPOSE:To remove malodor from stock raising excreta, etc., and to convert it in to an useful resources such as fertilizer by essentially constituting a deodolant material with a phosphoric acid compd. and iron sulfate which make a malodorous source nonvolatile and a magnesium compd. which makes the nonvolatile compd. hardly soluble. CONSTITUTION:This deodolant material is essentially composed of the phosphoric acid compd. and iron sulfate which make the malodorous source nonvolatile and the magnesium compd. which makes the nonvolatile compd. hardly soluble, In this case, calcium perphosphate and triple calcium superphosphate are used as the phosphoric acid compd., and magnesium sulfate, magnesium hydroxide, magnesium oxide and magnesium phosphate, etc., are used as the magnesium compd. And, the deodolant material consisting essentially of the phosphoric acid compd. and iron sulfate which make the malodorous source nonvolatile and the magnesium compd. which makes the nonvolatile compd. hardly soluble are added to the stock raising excreta, and after removing the malodor, the material is dehydrated and dried to make the fertilizer. In this case, the deodolant material is added to a sediment, etc., of the stock raising excreta together with a porous silicic substance, activated carbon, etc..

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、畜産排泄物をはじめと
する各種の廃棄物中のアンモニア、アミン、硫化水素、
メルカプタン、フェノールおよび揮発性有機酸などを不
揮発性の化合物に変化させ、さらに難溶化して、これら
を発生源とする悪臭を除去すると共に肥料として活用で
きるようにした悪臭物質の脱臭資材と、これを用いた脱
臭肥料化方法に関する。
The present invention relates to ammonia, amines, hydrogen sulfide, various kinds of wastes including livestock excrement,
A deodorant material for malodorous substances that changes mercaptan, phenol, volatile organic acids, etc. to non-volatile compounds and makes them less soluble to remove the malodorous substances originating from these and also can be used as fertilizer. The present invention relates to a method for producing a deodorant fertilizer.

【0002】[0002]

【従来の技術】畜産業においては、その排泄物から発生
する悪臭が著しく、さらに、この排泄物によって地下水
が汚染され、河川、湖沼が富栄養化する問題があり、環
境汚染の大きな原因となっている。この悪臭除去のた
め、従来から種々の改善方法が試みられており、例え
ば、家畜の飼料中に悪臭を吸着する物質を添加する方法
や、芳香剤を散布して悪臭をマスクする方法、あるいは
悪臭源を微生物によって分解する方法などが知られてい
る。しかし、従来の上記方法は、悪臭原因物質が動物の
種類や飼育管理の方法などによって大きく異なるために
多大な処理経費を要しながらも十分な効果が得られない
現状にある。
2. Description of the Related Art In the livestock industry, the offensive odor generated from the excrement is remarkable, and further, the excrement contaminates groundwater, resulting in eutrophication of rivers and lakes, which is a major cause of environmental pollution. ing. In order to remove this malodor, various improvement methods have been tried so far, for example, a method of adding a substance that adsorbs the malodor to the feed of livestock, a method of masking the malodor by spraying a fragrance, or a malodor. A method of decomposing a source with a microorganism is known. However, the above-mentioned conventional methods are in the present situation in which sufficient effect cannot be obtained even though a large processing cost is required because the malodorous substances differ greatly depending on the kind of animals and the method of breeding management.

【0003】悪臭源の吸着や分解を行う方法に代えて、
家畜の排泄量を少なくすることによって、悪臭を除去す
る方法も試みられており、蛋白質の給与量を減少させる
方法や、アミノ酸を与え、あるいはフィターゼによって
飼料中の有機態リンの利用率を高めて排泄量を減少させ
る方法などが提唱されているが実用化には程遠い。
Instead of a method of adsorbing or decomposing a malodorous source,
Attempts have also been made to eliminate malodors by reducing the amount of excreted livestock, and to reduce the amount of protein supplied, by giving amino acids, or by using phytase to increase the utilization rate of organic phosphorus in the feed. A method of reducing excretion has been proposed, but it is far from practical use.

【0004】一方、悪臭を除去して畜産環境を改善する
場合の実用面においては、低コストで環境改善ができる
こと、および処理物が一般の農業用肥料などとして広く
再利用できることなどが求められる。さらに、悪臭除去
処理後の排水を放流しても、自然環境を汚染しないこと
が必要とされる。
[0004] On the other hand, in terms of practical use in removing the bad odor to improve the livestock environment, it is required that the environment can be improved at a low cost and that the treated product can be widely reused as a general fertilizer for agriculture. Furthermore, it is necessary that the natural environment is not polluted even if the wastewater after the malodor removal treatment is discharged.

【0005】[0005]

【発明の解決課題】本発明は、従来の上記問題を解決す
るものであり、畜産排泄物などから悪臭を除去して、こ
れを肥料などの有用な資源に変える脱臭資材と、これを
用いた資材化方法を提供することを目的とする。本発明
者は、畜産排泄物中の基本的な悪臭源は、アンモニア、
アミン、硫化水素、メルカプタン、フェノールおよび揮
発性有機酸であり、これらにリン酸化合物ないし硫酸鉄
塩を加えて不揮発性化合物に変化させることによって悪
臭を抑制でき、さらにマグネシウム化合物を加えること
によって、これらが難溶化し、これを脱水すれば肥料と
して有効に利用でき、また処理排水を放流しても2次汚
染を生じる虞がないことを見出した。
DISCLOSURE OF THE INVENTION The present invention solves the above-mentioned problems of the prior art, and uses a deodorizing material that removes offensive odors from livestock excrement, etc., and turns them into useful resources such as fertilizers. The purpose is to provide a materialization method. The inventor has found that the basic odor source in livestock excrement is ammonia,
Amine, hydrogen sulfide, mercaptan, phenol and volatile organic acids, which can suppress odors by adding phosphoric acid compounds or iron sulfates to non-volatile compounds, and by adding magnesium compounds, these It has been found that the water becomes insoluble and can be effectively used as a fertilizer if it is dehydrated, and there is no risk of causing secondary pollution even if the treated wastewater is discharged.

【0006】[0006]

【発明の構成】本発明は上記知見に基づくものであり、
本発明によれば以下の構成からなる脱臭資材とそれを用
いた脱臭資材化方法が提供される。 (1)悪臭源を不揮発性化するリン酸化合物と硫酸鉄
塩、および不揮発性化合物を難溶化するマグネシウム化
合物を主成分とする脱臭資材。 (2)リン酸化合物として、過リン酸石灰、重過リン酸
石灰を用いる上記(1)の脱臭資材。 (3)マグネシウム化合物として、硫酸マグネシウム、
水酸化マグネシウム、酸化マグネシウムおよびリン酸マ
グネシウム類を用いる上記(1) または(2) の脱臭資材。 (4)悪臭源を不揮発性化するリン酸化合物と硫酸鉄
塩、および不揮発性化合物を難溶化するマグネシウム化
合物を主成分とする脱臭資材を畜産排泄物に添加し、悪
臭を除去した後に脱水、乾燥して肥料化する脱臭肥料化
方法。 (5)上記脱臭資材を多孔質ケイ酸物質、活性炭、凝集
剤、殺菌剤または芳香剤と共に畜産排泄物の堆積物、貯
蔵用ないし散布用タンクあるいは流出溝に添加する上記
(4)の脱臭肥料化方法。
The present invention is based on the above findings,
According to the present invention, there are provided a deodorizing material having the following constitution and a deodorizing material producing method using the deodorizing material. (1) A deodorizing material mainly composed of a phosphate compound and an iron sulfate salt that make a malodor source non-volatile, and a magnesium compound that makes a non-volatile compound hardly soluble. (2) The deodorizing material according to (1) above, which uses lime superphosphate or lime superphosphate as the phosphate compound. (3) As the magnesium compound, magnesium sulfate,
The deodorizing material according to (1) or (2) above, which uses magnesium hydroxide, magnesium oxide and magnesium phosphates. (4) A deodorizing material containing a phosphate compound and an iron sulfate salt that make the malodor source non-volatile as the main component and a magnesium compound that makes the non-volatile compound hardly soluble is added to livestock excrement to remove the malodor, and then dehydrated. A deodorizing fertilizer method of drying and fertilizing. (5) The above-mentioned deodorizing material is added together with a porous silicic acid substance, activated carbon, a flocculant, a bactericide or an fragrance to a deposit of livestock excrement, a storage or spraying tank or an outflow ditch.
The deodorizing fertilizer method of (4).

【0007】[0007]

【具体的な説明】畜産排泄物などに含まれる悪臭原因物
質の種類と含有量は、畜産動物の種類や飼育環境によっ
て異なるが、各動物の排泄物に共通な基本的な悪臭物質
は、アンモニア、トリメチルアミン、硫化水素、メチル
メルカプタン、硫化メチル、揮発性有機酸類である。こ
れらのうち、アンモニアは本発明の脱臭資材に含有され
るリン酸化合物によってリン酸二アンモン[(NH4 ) 2 HP
O 4 ] に変わり、不揮発性化合物となるのでアンモニア
臭が除去される。ここでリン酸二アンモンは水溶性であ
るが、さらに本発明の脱臭資材に含まれるマグネシウム
化合物によって、pH 6.0〜8.5 において、リン酸二ア
ンモンはリン酸苦土アンモン[MgNH 4 PO4 ] に変わり、
難溶性化する。これを脱水することにより肥料として利
用することができる。また、マグネシウム化合物は排泄
物中の悪臭成分である酪酸類について、これを無臭の酪
酸マグネシウムに変化させるなどの効果も有する。リン
酸化合物としては、過リン酸石灰、重過リン酸石灰など
を用いることができる。またマグネシウム化合物として
は、硫酸マグネシウム、水酸化マグネシウム、酸化マグ
ネシウムおよびリン酸マグネシウム類などを用いること
ができる。なお、リン酸化合物として過リン酸石灰を用
いた場合、過リン酸石灰には約50wt%以上の硫酸カル
シウムが存在しており、これが脱臭処理物の凝集剤とし
ても作用する。また、リン酸マグネシウム類を使用する
場合には、市販の肥料用過リン酸石灰や重過リン酸石灰
にリン酸マグネシウム相当量の酸化マグネシウムまたは
水酸化マグネシウムを添加して使用することにより、コ
ストの低下および処理工程の省力化が図れる。
[Detailed description] The type and content of the offensive odor-causing substances contained in livestock excrement differ depending on the type of livestock animal and the breeding environment, but the basic malodorous substance common to the excrement of each animal is ammonia. , Trimethylamine, hydrogen sulfide, methyl mercaptan, methyl sulfide, volatile organic acids. Of these, ammonia is diammonium phosphate [(NH 4 ) 2 HP due to the phosphate compound contained in the deodorizing material of the present invention.
It changes to O 4 ] and becomes a non-volatile compound, so the ammonia odor is removed. Here, diammonium phosphate is water-soluble, but due to the magnesium compound contained in the deodorizing material of the present invention, diammonium phosphate changes to magnesia ammonium phosphate [MgNH 4 PO 4 ] at pH 6.0 to 8.5. ,
It becomes insoluble. By dehydrating this, it can be used as fertilizer. In addition, the magnesium compound has an effect of converting butyric acid which is a malodorous component in excrement into odorless magnesium butyrate. As the phosphoric acid compound, it is possible to use lime superphosphate, lime superphosphate and the like. As the magnesium compound, magnesium sulfate, magnesium hydroxide, magnesium oxide, magnesium phosphates and the like can be used. When lime superphosphate is used as the phosphate compound, about 50 wt% or more of calcium sulfate exists in the lime superphosphate, and this also acts as a flocculant for the deodorized product. Also, when using magnesium phosphates, by adding magnesium oxide or magnesium hydroxide in an amount equivalent to magnesium phosphate to commercially available fertilizer superphosphate or hyperperphosphate, the cost can be reduced. Can be reduced and the processing steps can be saved.

【0008】畜産排泄物中の硫黄化合物は、嫌気性下で
還元されて硫化水素を発生し、これが悪臭源となる。本
発明の脱臭資材に含有される硫酸鉄塩は、この硫化水素
と反応して不揮発性の硫化物を生じ、悪臭を除去する。
また他の悪臭発生源である低級脂肪酸も硫酸鉄塩と反応
して無臭の鉄化合物となる。硫酸鉄塩としては、硫酸第
一鉄(FeSO4 ・7H2 O )などを用いることができる。
Sulfur compounds in livestock excrement are reduced anaerobically to generate hydrogen sulfide, which becomes a source of malodor. The iron sulfate salt contained in the deodorizing material of the present invention reacts with this hydrogen sulfide to form a non-volatile sulfide, and removes a bad odor.
Further, lower fatty acids, which are other sources of malodor, also react with iron sulfate to form odorless iron compounds. As the iron sulfate salt, ferrous sulfate (FeSO 4 .7H 2 O) or the like can be used.

【0009】本発明の脱臭資材中のリン酸化合物、硫酸
鉄塩およびマグネシウム化合物の配合量は、使用される
悪臭物質の種類によって適宜定められるが、概ね、以下
の配合量とすれば良い。 (1) 過リン酸石灰(リン酸17.0%) 650g 酸化マグネシウム(MgO 90%) 50g 硫酸第一鉄(FeSO4 ・7H2 O ) 350g (2) 重過リン酸石灰(リン酸42%) 360g 硫酸苦土(MgO 25%) 280g 硫酸第一鉄 360g 酸化マグネシウム(MgO 90%) 200g (3) 重過リン酸石灰 1.1g 硫酸苦土 0.5g 硫酸第一鉄 1.0g 酸化マグネシウム 0.2g また本発明の脱臭資材は畜産排泄物等に対して悪臭発生
源を不揮発性化および難溶性化するに足りる量を使用す
るが、例えば、後述する実施例に示すように、窒素29
0gを含有する乳牛の排泄物スラリー50リットルに対して
本発明の脱臭資材を800g〜2.5Kg程度添加すれば
良い。
The compounding amounts of the phosphoric acid compound, the iron sulfate salt and the magnesium compound in the deodorizing material of the present invention are appropriately determined depending on the kind of the malodorous substance to be used, but the following compounding amounts are generally acceptable. (1) Over phosphate of lime (17.0 percent phosphoric acid) 650 g magnesium oxide (90% MgO) 50 g of ferrous sulfate (FeSO 4 · 7H 2 O) 350g (2) monocalcium phosphate (42% phosphoric acid) 360 g Magnesium sulfate (MgO 25%) 280 g Ferrous sulfate 360 g Magnesium oxide (MgO 90%) 200 g (3) Lime superphosphate 1.1 g Magnesium sulfate 0.5 g Ferrous sulfate 1.0 g Magnesium oxide 0. 2 g The deodorizing material of the present invention is used in an amount sufficient to render the malodor source non-volatile and sparingly soluble in livestock excrement and the like. For example, as shown in Examples described later, nitrogen 29
It is sufficient to add about 800 g to 2.5 kg of the deodorizing material of the present invention to 50 liters of dairy cow excrement slurry containing 0 g.

【0010】本発明の脱臭資材はゼオライト、トバモラ
イトなどの多孔質ケイ酸物質と併用することにより、脱
臭効果を一層高めることができる。従来、ゼオライト、
トバモライトなどの多孔質ケイ酸物質を悪臭物質に散布
して悪臭源や水分を吸着させることにより悪臭を軽減す
ることが行われているが、吸着能力に限界があり、また
添加量も限られることから十分な悪臭除去効果が得られ
ない。ところが、本発明の脱臭資材にゼオライト、トバ
モライトなどの多孔質ケイ酸物質を加えて使用すれば、
本発明の脱臭資材によって悪臭源の殆どは不揮発性化さ
れるので、僅かに悪臭源が残留する場合、これが上記多
孔質ケイ酸物質に吸着され、悪臭除去効果が一層向上す
る。
When the deodorizing material of the present invention is used in combination with a porous silicic acid substance such as zeolite or tobermorite, the deodorizing effect can be further enhanced. Conventionally, zeolite,
It has been attempted to reduce the malodor by spraying a porous silicic acid substance such as tobermorite on the malodorous substance to adsorb the malodorous source and moisture, but the adsorption capacity is limited and the addition amount is also limited. Does not provide sufficient odor removal effect. However, if the zeolite is added to the deodorizing material of the present invention, and a porous silicate substance such as tobermorite is used,
Since most of the malodorous source is made non-volatile by the deodorizing material of the present invention, when a slight malodorous source remains, it is adsorbed by the porous silicic acid substance and the malodorous removing effect is further improved.

【0011】本発明の脱臭資材は、畜産排泄物の流出溝
などに所定量を徐々に添加して使用しても良く、または
排泄物の堆積物や、排泄物の貯蔵タンクや散布用タンク
に直接に必要量を投入して使用しても良い。さらに、本
発明の脱臭資材と共に活性炭、凝集剤、殺菌剤および芳
香剤などを配合して使用しても良い。これらの添加によ
り本発明の脱臭効果が増強され、また各添加剤の効果も
損なわれない。
The deodorizing material of the present invention may be used by gradually adding a predetermined amount to an outflow ditch of livestock excrement, or in a deposit of excrement, a storage tank of the excrement or a spraying tank. You may throw in and use the required amount directly. Further, activated carbon, a coagulant, a bactericide, an aromatic and the like may be blended and used together with the deodorizing material of the present invention. The addition of these enhances the deodorizing effect of the present invention and does not impair the effect of each additive.

【0012】本発明の脱臭資材によって悪臭が除去され
た畜産排泄物は肥料として有効に利用することができ
る。畜産農家は家畜の飼料用牧草を栽培するために大量
の肥料を必要とする。そこで、一般に、家畜排泄物など
を有機肥料として利用するために、この排泄物を敷ワラ
等と共に畜舎から取出し、堆積して堆肥化する。ところ
が、排泄物などの悪臭が酷く、作業環境が著しく悪化す
る問題があった。本発明の脱臭資材を使用すれば、悪臭
が効果的に除去されるので堆肥化の期間中、このような
問題を生じない。さらに、本発明の脱臭資材を用いれ
ば、畜産排泄物中のアンモニア、リン酸およびカリ成分
は難溶性化合物に変えて含有されており、しかもこれら
は緩効性肥料としても有用なリン酸苦土アンモンあるい
はリン酸苦土カリとして含有されているので、本発明の
脱臭資材を加えて悪臭除去したものを脱水、乾燥すれ
ば、そのまま有効な窒素、リン酸、カリおよび苦土肥料
として利用することができる。なお、硫酸鉄塩はリン酸
化合物を十分量配合することにより、リン酸無効化作用
が抑制され、作物への悪影響がなく、むしろ作物に鉄分
を供給する効果が認められる。
The livestock excrement from which the malodor has been removed by the deodorizing material of the present invention can be effectively used as fertilizer. Livestock farmers need large amounts of fertilizer to grow feed forage for livestock. Therefore, in general, in order to utilize livestock excrement and the like as organic fertilizer, this excrement is taken out from a livestock shed together with spread straws, etc., and accumulated and composted. However, there is a problem that a bad odor such as excrement is severe and the working environment is significantly deteriorated. When the deodorizing material of the present invention is used, the bad odor is effectively removed, and therefore such a problem does not occur during the composting period. Furthermore, when the deodorizing material of the present invention is used, ammonia, phosphoric acid and potassium components in livestock excrement are contained in place of sparingly soluble compounds, and these are also useful as a slow-release fertilizer. Since it is contained as ammon or potassium phosphate phosphate, it can be used as effective nitrogen, phosphate, potash and magnesium fertilizer if dehydrated and dried after removing the bad odor by adding the deodorizing material of the present invention. You can It should be noted that when the iron sulfate is blended with a sufficient amount of a phosphoric acid compound, the phosphoric acid inactivating effect is suppressed, there is no adverse effect on the crop, and rather the effect of supplying iron to the crop is observed.

【0013】[0013]

【実施例】以下に本発明の試験例と実施例を示す。な
お、本実施例は例示であり本発明の範囲を限定するもの
ではない。 試験例 窒素290gを含有する乳牛の排泄物スラリーを原液と
し、この原液100gに表1に示す量の過リン酸石灰、重過
リン酸石灰、硫酸第一鉄、硫酸苦土、水酸化マグネシウ
ムおよび酸化マグネシウムを添加し、その脱臭効果を調
べた。この結果を表1に纏めて示した。また同様の原液
100gに表2に示す本発明に係る脱臭資材(試料No11)を
添加して、その脱臭効果を調べた。この結果を表2に示
した。表示するように、上記添加剤は優れた脱臭効果を
示し、特に、本発明の脱臭資材は上記添加剤を個々に使
用したものよりも優れた脱臭効果が確認された。
EXAMPLES Test examples and examples of the present invention will be shown below. It should be noted that this embodiment is merely an example and does not limit the scope of the present invention. Test Example A dairy cow excrement slurry containing 290 g of nitrogen was used as an undiluted solution, and 100 g of this undiluted solution was used in the amounts shown in Table 1 for lime superphosphate, lime superphosphate, ferrous sulfate, magnesium sulfate, magnesium hydroxide and Magnesium oxide was added and the deodorizing effect was investigated. The results are summarized in Table 1. Similar stock solution
The deodorizing material according to the present invention (Sample No. 11) shown in Table 2 was added to 100 g, and the deodorizing effect was examined. The results are shown in Table 2. As shown, the above-mentioned additives exhibited an excellent deodorizing effect, and in particular, the deodorizing material of the present invention was confirmed to have a deodorizing effect superior to those using the above-mentioned additives individually.

【0014】[0014]

【表1】 [Table 1]

【0015】[0015]

【表2】 [Table 2]

【0016】実施例1 市販過リン酸石灰(SP17.0%)650Kg、市販肥料用酸
化マグネシウム(MgO90%含有)50Kgおよび硫酸第一
鉄(FeSO4 ・7H2 O )350Kgを混合した本発明の脱臭
資材2.5Kgに水を加えてスラリーとし、これを窒素2
90gを含有する乳牛排泄スラリー50リットル中に添加混
合した。排泄スラリ−のpHは7.6 であったが、混合10
〜15分経過後には排泄物の臭気は消失した。処理後のp
Hは 6.5であった。処理後、反応物の回収量は、無水物
換算で約3.0Kgであった。回収処理物中の栄養成分
は、無水物換算でN: 9.0%、P: 9.1%、K
O: 9.0%、MgO: 3.2%およびFe: 3.5%であっ
た。このものを畑10aあたり 400Kg相当量を施肥したポ
ットを用い、コマツナを栽培し、硫安、過石および硫加
を同一成分になるように添加したものとの生育量を比較
したところ、一般化学肥料を用いた場合の100に対し
て、本発明の肥料を用いたものは115の高い収量指数
を示した。
EXAMPLE 1 Commercially available lime superphosphate (SP17.0%) 650 kg, commercial magnesium oxide for fertilizer (containing MgO 90%) 50 kg and ferrous sulfate (FeSO 4 .7H 2 O) 350 kg were mixed. Water was added to 2.5 kg of deodorizing material to make a slurry, and this was added with nitrogen 2
The mixture was added and mixed into 50 liters of dairy cow excretion slurry containing 90 g. The pH of the excretion slurry was 7.6, but mixed 10
After about 15 minutes, the odor of excrement disappeared. P after processing
H was 6.5. After the treatment, the recovered amount of the reaction product was about 3.0 kg in terms of anhydride. The nutritional components in the recovered treated product are N: 9.0%, P 2 O 5 : 9.1%, K 2 in terms of anhydride.
O: 9.0%, MgO: 3.2% and Fe: 3.5%. Using this pot fertilized with an amount equivalent to 400 kg per field 10a, Komatsuna was cultivated, and the growth rate was compared with that obtained by adding ammonium sulfate, overstone, and sulphate to the same components. With the fertilizer of the invention, a high yield index of 115 was shown, compared to 100 when used.

【0017】実施例2 市販重過リン酸石灰(SP42%)360Kg、肥料用硫酸苦
土(MgO 25%含有)280Kgおよび硫酸第一鉄(FeSO4
・7H2 O )360Kgを混合したもの800gを水に懸濁
させた後、窒素290gを含有する乳牛排泄スラリー5
0リットル (pH7.6)中に添加混合した。混合10〜15分後のp
Hは約 6.3であった。上記処理によりアンモニア臭は完
全に消失したが、排泄物特有の臭気が僅かながら認めら
れた。そこで、これに市販肥料用酸化マグネシウム粉末
(MgO 90%含有)200gを添加混合した結果、悪臭は
消失した。処理後のpHは 6.7であった。回収した反応
処理物の量は、無水物換算で1.5Kgであった。得られ
た処理物中の栄養成分量は乾物換算でN:19.0%、P
:11.3%,KO:16.0%、MgO:15.1%および
Fe: 3.5%であった。このものは、簡単な造粒機でバ
インダーを使用する必要もなく容易に造粒することがで
きた。造粒・乾燥したものはミネラル入り高度複合肥料
として、牧草および一般作物の栽培に用いたところ、実
施例1と同様に高い収量を達成した。
Example 2 360 kg of commercially available lime superphosphate (SP42%), 280 kg of ferric sulfate magnesia (containing 25% of MgO) and ferrous sulfate (FeSO 4)
・ 7H 2 O) 360 kg mixed 800 g, suspended in water, and then dairy cow excretion slurry 5 containing 290 g nitrogen 5
The mixture was added and mixed in 0 liter (pH 7.6). 10 to 15 minutes after mixing
H was about 6.3. The ammonia odor was completely eliminated by the above treatment, but a slight odor peculiar to excrement was recognized. Then, as a result of adding and mixing 200 g of magnesium oxide powder for commercial fertilizer (containing 90% of MgO) thereto, the malodor disappeared. The pH after the treatment was 6.7. The amount of the recovered reaction product was 1.5 kg in terms of anhydride. The amount of nutritional components in the obtained treated product was N: 19.0%, P 2 in terms of dry matter.
O 5: 11.3%, K 2 O: 16.0%, MgO: 15.1% and Fe: was 3.5%. This product could be easily granulated with a simple granulator without the need of using a binder. When the granulated and dried product was used as a high-performance compound fertilizer containing minerals for the cultivation of grass and general crops, a high yield was achieved as in Example 1.

【0018】[0018]

【発明の効果】本発明の脱臭資材によれば、畜産排泄物
などの悪臭を効果的に除去することができ、しかも悪臭
源は難溶性化合物として含有されるので、処理排水を放
流しても環境を2次汚染する問題がなく、また悪臭を除
去した非処理物中には、窒素、リン酸、カリなどの肥料
成分が含まれるので、これを緩効肥料として有効利用す
ることができる。
According to the deodorizing material of the present invention, it is possible to effectively remove the malodor of livestock excrement and the like, and the malodor source is contained as a sparingly soluble compound. Since there is no problem of secondary pollution of the environment and the untreated product from which the bad odor is removed contains fertilizer components such as nitrogen, phosphoric acid and potassium, it can be effectively used as a slow-release fertilizer.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01D 53/81 B01J 20/04 C B09B 3/00 ZAB C05F 3/00 7537−4H 17/00 C09K 3/00 S ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location B01D 53/81 B01J 20/04 C B09B 3/00 ZAB C05F 3/00 7537-4H 17/00 C09K 3/00 S

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】悪臭源を不揮発性化するリン酸化合物と硫
酸鉄塩、および不揮発性化合物を難溶化するマグネシウ
ム化合物を主成分とする脱臭資材。
1. A deodorizing material containing a phosphate compound and an iron sulfate salt for making a malodor source non-volatile, and a magnesium compound for making a non-volatile compound hardly soluble, as main components.
【請求項2】リン酸化合物として、過リン酸石灰、重過
リン酸石灰を用いる請求項1の脱臭資材。
2. The deodorizing material according to claim 1, wherein lime superphosphate and lime superphosphate are used as the phosphate compound.
【請求項3】マグネシウム化合物として、硫酸マグネシ
ウム、水酸化マグネシウム、酸化マグネシウムおよびリ
ン酸マグネシウム類を用いる請求項1または2の脱臭資
材。
3. The deodorizing material according to claim 1, wherein magnesium sulfate, magnesium hydroxide, magnesium oxide and magnesium phosphates are used as the magnesium compound.
【請求項4】悪臭源を不揮発性化するリン酸化合物と硫
酸鉄塩、および不揮発性化合物を難溶化するマグネシウ
ム化合物を主成分とする脱臭資材を畜産排泄物に添加
し、悪臭を除去した後に脱水、乾燥して肥料化する脱臭
肥料化方法。
4. A deodorizing material containing, as a main component, a phosphate compound and an iron sulfate salt which make a malodor source non-volatile and a magnesium compound which makes the non-volatile compound hardly soluble is added to livestock excrement to remove the malodor. A deodorizing fertilizer method of dehydrating, drying and fertilizing.
【請求項5】上記脱臭資材を多孔質ケイ酸物質、活性
炭、凝集剤、殺菌剤または芳香剤と共に畜産排泄物の堆
積物、貯蔵用ないし散布用タンクあるいは流出溝に添加
する請求項4の脱臭肥料化方法。
5. The deodorizing agent according to claim 4, wherein the deodorizing material is added to a sediment of livestock excrement, a storage or spraying tank, or an outflow ditch together with a porous silicic acid substance, activated carbon, a flocculant, a bactericide or an aromatic agent. Fertilization method.
JP35098193A 1993-12-28 1993-12-28 Deodorant material and its deodorizing and fertilizer making method Pending JPH07185318A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP35098193A JPH07185318A (en) 1993-12-28 1993-12-28 Deodorant material and its deodorizing and fertilizer making method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP35098193A JPH07185318A (en) 1993-12-28 1993-12-28 Deodorant material and its deodorizing and fertilizer making method

Publications (1)

Publication Number Publication Date
JPH07185318A true JPH07185318A (en) 1995-07-25

Family

ID=18414232

Family Applications (1)

Application Number Title Priority Date Filing Date
JP35098193A Pending JPH07185318A (en) 1993-12-28 1993-12-28 Deodorant material and its deodorizing and fertilizer making method

Country Status (1)

Country Link
JP (1) JPH07185318A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20000019613A (en) * 1998-09-14 2000-04-15 김형벽 Method for purifying wastewater using struvite precipitation.
KR100371522B1 (en) * 2000-07-19 2003-02-06 정연구 Manufacture Method of High Quality Manure Using Struvite Synthesis Reactction
KR100393734B1 (en) * 2000-07-18 2003-08-09 홍국선 Ceramic Deodorant
JP2005330143A (en) * 2004-05-19 2005-12-02 Onoda Chemical Industry Co Ltd Phosphoric acid-added mixed organic fertilizer
CN103011984A (en) * 2013-01-04 2013-04-03 福建省邵武市榕丰化工有限公司 Liquid superphosphate active porous agent
KR20190103648A (en) * 2018-02-28 2019-09-05 농업회사법인 주식회사 과농 Basic odor removing effect reinforcing composition and manufacturing method thereof
KR102102727B1 (en) * 2019-10-24 2020-05-29 주식회사 풍산비료 Manufacturing method for slowing compost release using livestock excretion and slowing compost manufactured thereby

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20000019613A (en) * 1998-09-14 2000-04-15 김형벽 Method for purifying wastewater using struvite precipitation.
KR100393734B1 (en) * 2000-07-18 2003-08-09 홍국선 Ceramic Deodorant
KR100371522B1 (en) * 2000-07-19 2003-02-06 정연구 Manufacture Method of High Quality Manure Using Struvite Synthesis Reactction
JP2005330143A (en) * 2004-05-19 2005-12-02 Onoda Chemical Industry Co Ltd Phosphoric acid-added mixed organic fertilizer
CN103011984A (en) * 2013-01-04 2013-04-03 福建省邵武市榕丰化工有限公司 Liquid superphosphate active porous agent
CN103011984B (en) * 2013-01-04 2014-03-19 福建省邵武市榕丰化工有限公司 Liquid superphosphate active porous agent
KR20190103648A (en) * 2018-02-28 2019-09-05 농업회사법인 주식회사 과농 Basic odor removing effect reinforcing composition and manufacturing method thereof
KR102102727B1 (en) * 2019-10-24 2020-05-29 주식회사 풍산비료 Manufacturing method for slowing compost release using livestock excretion and slowing compost manufactured thereby

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