JPH03126688A - Treating agent for converting night soil into organic fertilizer and treatment - Google Patents

Treating agent for converting night soil into organic fertilizer and treatment

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Publication number
JPH03126688A
JPH03126688A JP1263581A JP26358189A JPH03126688A JP H03126688 A JPH03126688 A JP H03126688A JP 1263581 A JP1263581 A JP 1263581A JP 26358189 A JP26358189 A JP 26358189A JP H03126688 A JPH03126688 A JP H03126688A
Authority
JP
Japan
Prior art keywords
manure
organic fertilizer
treatment
treatment agent
sodium
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.)
Granted
Application number
JP1263581A
Other languages
Japanese (ja)
Other versions
JP2619073B2 (en
Inventor
Isamu Nakamura
勇 中村
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.)
HONMACHI KK
Original Assignee
HONMACHI KK
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Filing date
Publication date
Application filed by HONMACHI KK filed Critical HONMACHI KK
Priority to JP1263581A priority Critical patent/JP2619073B2/en
Publication of JPH03126688A publication Critical patent/JPH03126688A/en
Application granted granted Critical
Publication of JP2619073B2 publication Critical patent/JP2619073B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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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

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  • Fertilizers (AREA)

Abstract

PURPOSE:To enhance deodorizing effect and to enable immediate fertilization by adding FeSO4.7H2O, sodium L-ascorbate and fly ash or zeolite powder. CONSTITUTION:FeSO4.7H2O is blended with 0.1-20wt.% sodium L-ascorbate basing on the amt. of FeSO4 and 20-100wt.% fly ash or zeolite powder to obtain a treating agent for converting night soil into an org. fertilizer. This treating agent is added to night soil by 30-200g per 100l night soil.

Description

【発明の詳細な説明】 産業上の利用分野 この発明は、人や家畜の糞尿を農作物を始めとする植物
育成に非常に有用で且つ取扱い性のよい有機肥料に転化
させる処理剤及び処理方法に関する。
DETAILED DESCRIPTION OF THE INVENTION Field of Industrial Application This invention relates to a treatment agent and a treatment method for converting human and livestock manure into organic fertilizer that is very useful for growing crops and other plants and is easy to handle. .

従来の技術 古来より糞尿は下肥として肥料の重要な地位を占めてい
たが、悪臭、取扱い性、施肥効率、衛生観念等より敬遠
され、近代農業では化学肥料に代替されて殆ど使用され
ていない。しかるに、近年においては、食品の安全性や
味の良さ等の面より有機農法が見直されつ\あり、これ
に伴って有機肥料源として下肥が再び着目されている。
Conventional technology Since ancient times, manure has played an important role as a fertilizer, but it has been shunned due to its bad odor, ease of handling, fertilizer application efficiency, and hygiene, and is now almost no longer used in modern agriculture as it has been replaced by chemical fertilizers. . However, in recent years, organic farming methods have been reconsidered in terms of food safety and good taste, and with this, manure is once again attracting attention as a source of organic fertilizer.

一方、我国におけるトイレの水洗化率は、昭和63年度
住宅統計調査速報及び全浄連News、1989年第4
1号によると、し尿浄化檜による処理を含めても都市部
を中心に65,8%に過ぎない。残りの全戸数の1/3
強より発生するし尿は、大部分が市町村単位で莫大な費
用を投じて収集・処理されており、その総量は一日平均
76.00011に達し、浄化槽汚泥を含めると10万
11/日(昭和61年度)にもなることが報告されてい
る。
On the other hand, the flushing rate of toilets in Japan is reported in the 1989 Housing Statistics Survey Bulletin and Zenjoren News, 1989
According to No. 1, even if treatment using cypress is included, only 65.8% of human waste is purified, mainly in urban areas. 1/3 of the total number of remaining units
Most of the human waste generated in the region is collected and treated at the municipal level at huge expense, and the total amount reaches an average of 76,000,000 yen per day, and if septic tank sludge is included, it exceeds 100,000,000 sludge per day (Showa era). It has been reported that this will occur in 1961).

従って、肥料として下肥を大々的に復活したとしても将
来的にも充分な供給余力があると共に、下肥として利用
した分だけ上記の収集・処理に要する費用が軽減される
ことになる。
Therefore, even if manure is revived as fertilizer on a large scale, there will be sufficient supply capacity in the future, and the cost required for collection and processing will be reduced by the amount used as manure.

しかしながら、糞尿を単にそのま\下肥として用いるの
では旧態に戻るだけであり、悪臭を始めとするかっての
衰退の要因である様々な問題点が何ら解決されないこと
になる。
However, simply using excrement as it is as manure will simply return to the old state, and the various problems that were the cause of the decline, including the bad odor, will not be solved at all.

従来、糞尿や生ゴミ等の悪臭防止に有効で且つ低廉な脱
臭処理剤として鉄(II)化合物とL−アスコルビン酸
とを組合わせたものが提案(特公昭61−43091号
)され、また鶏糞の飼料化用処理剤につき硫酸第1鉄と
フライアッシュまたは乾燥天然ゼオライト微粉末との混
合物が消臭作用を有するものとして提案(特公昭46−
34724号、同5C1−32979号)されている。
Conventionally, a combination of an iron (II) compound and L-ascorbic acid has been proposed as an effective and inexpensive deodorizing treatment agent for preventing bad odors from excrement, garbage, etc. (Japanese Patent Publication No. 61-43091). A mixture of ferrous sulfate and fly ash or dried natural zeolite fine powder was proposed as having a deodorizing effect as a treatment agent for feed.
No. 34724, No. 5C1-32979).

そして、これら処理剤によればアンモニア、硫化水素、
メルカプタン類の悪臭が顕著に脱臭されることが認めら
れており、その作用は、鉄(n)イオンがアンモニアと
錯体を形成し、この錯体が含硫黄臭気成分との間でFe
−8結合を形成して該成分を固定化することによると推
定される。
According to these processing agents, ammonia, hydrogen sulfide,
It has been recognized that the bad odor of mercaptans is significantly deodorized, and the effect is that iron (n) ions form a complex with ammonia, and this complex forms a complex with sulfur-containing odor components.
This is presumed to be due to the immobilization of the component by forming -8 bonds.

発明が解決しようとする課題 しかしながら、上記両処理剤は、人の糞尿に対する脱臭
にも有効と考えられるが、上記糞尿を下肥として有機肥
料化するための処理用には充分なものといえない。すな
わち、有機肥料化においては、環境衛生面では使捨から
の汲み取りより施肥、更には施肥後に至るまでの悪臭の
防止を要し、しかも農業経営上からは化学肥料農法にあ
る程度対抗するために施肥効率及び作業能率を高めると
共に、土壌への影響を配慮して作物の収量増大及び品質
向上を図る必要かある。
Problems to be Solved by the Invention However, although both of the above-mentioned treatment agents are considered to be effective in deodorizing human excrement, they cannot be said to be sufficient for processing the above-mentioned excrement to convert it into organic fertilizer as a bottom fertilizer. . In other words, in terms of environmental hygiene, organic fertilizer requires application rather than fertilization from disposable waste, and prevention of bad odors even after fertilization, and from an agricultural management standpoint, it is necessary to apply fertilizer to some extent to counter chemical fertilizer farming. In addition to increasing efficiency and work efficiency, it is necessary to increase crop yield and improve quality while taking into account the impact on the soil.

この発明は、上述の事情に鑑み、処理時点より施肥後に
至るまで長期間にわたり強力な脱臭作用を持続できると
共に、処理後に直ちに施肥可能であり、しかも土壌の性
状及び組成を農作物生育に好適な条件に設定できる糞尿
の有機肥料化処理剤と処理方法を提供し、もって安全で
高品質の農作物を高収量で得ることを可能にすると同時
に、糞尿の下肥としての利用促進とこれによるし尿処理
費の低減を図ることを目的とする。
In view of the above-mentioned circumstances, the present invention is capable of maintaining a strong deodorizing effect for a long period of time from the time of treatment to after fertilization, and also enables fertilization to be applied immediately after treatment, while maintaining soil properties and composition under conditions suitable for crop growth. We provide a treatment agent and treatment method for converting manure into organic fertilizer that can be set as fertilizer, thereby making it possible to obtain safe, high-quality agricultural products with high yields.At the same time, we promote the use of manure as a bottom fertilizer and reduce the cost of manure treatment. The purpose is to reduce the

課題を解決するための手段 上記目的を達成する手段として、この発明における糞尿
の有機肥料化処理剤は、硫酸第1鉄と、L−アスコルビ
ン酸ナトリウムと、フライアッシュまたはゼオライト粉
末とを主成分とする構成を採用したものである。また、
この発明における糞尿の有機肥料化処理方法は、上記処
理剤を糞尿に添加混合することを特徴としている。
Means for Solving the Problems As a means for achieving the above objects, the present invention provides a treatment agent for converting manure into organic fertilizer, which contains ferrous sulfate, sodium L-ascorbate, and fly ash or zeolite powder as main components. This configuration adopts the following configuration. Also,
The method for converting manure into organic fertilizer according to the present invention is characterized in that the above-mentioned treatment agent is added to and mixed with manure.

なお、この発明においては、無水物換算硫酸第1鉄に対
して、L−アスコルビン酸ナトリウムが0.1〜20重
量%、フライアッシュまたはゼオライト粉末が20〜1
00重量%、それぞれ配合されてなる上記処理剤、なら
びに処理剤の添加量が糞尿100uに対して30〜20
0gの範囲である上記処理方法、を共に好適態様として
いる。
In addition, in this invention, sodium L-ascorbate is 0.1 to 20% by weight and fly ash or zeolite powder is 20 to 1% by weight based on ferrous sulfate in terms of anhydride.
00% by weight, and the amount of the processing agent added is 30 to 20% by weight per 100U of excrement.
Both of the above treatment methods in which the amount is in the range of 0 g are preferred embodiments.

発明の具体的構成と作用 処理剤の一成分である硫酸第1鉄は、例えば二酸化チタ
ン製造工程等の含硫黄鉱石を原料とする無機物質製造工
程より副生物として大量に製出するものであり、一般に
潮解性を有する青緑色結晶である7水塩(FeSO4−
7H20)として安価に人手できる。
Specific Structure and Effects of the Invention Ferrous sulfate, which is a component of the treatment agent, is produced in large quantities as a by-product from an inorganic material manufacturing process using sulfur-containing ore as a raw material, such as a titanium dioxide manufacturing process. , heptahydrate (FeSO4-
7H20), it can be done manually at low cost.

しかして、この硫酸第1鉄は水に溶けて鉄(n)イオン
(Fe”)を生じるため、処理剤を糞尿に添加した際、
該鉄(II)イオンがアンモニア(NH3)と反応して
Fe”+4NH3→[:Fe (NH3) 4 ) 2
+の如く錯体を形成し、この錯体が含硫黄悪臭成分と反
応してFe−8結合によって該成分を固定化することに
より、アンモニア、硫化水素、メルカプタン類等の悪臭
の防止が果される。また、この硫酸第1鉄を含む処理剤
で処理された糞尿を下肥として施肥することにより、土
壌に不足勝ちの鉄分が硫酸第1鉄由来の吸収の早い鉄(
n)の形で供給されることになり、農作物の生育に好結
果を与える。
However, this ferrous sulfate dissolves in water and produces iron (n) ions (Fe''), so when a treatment agent is added to excrement,
The iron(II) ion reacts with ammonia (NH3) to form Fe"+4NH3→[:Fe (NH3) 4 ) 2
By forming a complex such as +, this complex reacts with a sulfur-containing malodorous component, and fixes the component through Fe-8 bonds, thereby preventing malodors such as ammonia, hydrogen sulfide, and mercaptans. In addition, by fertilizing the manure treated with a treatment agent containing ferrous sulfate as a subfertilizer, the iron that is likely to be deficient in the soil can be replaced with quickly absorbed iron derived from ferrous sulfate (
n), which gives good results to the growth of agricultural crops.

L−アスコルビン酸ナトリウムは、一般にビタミンCと
して知られるL−アスコルビン酸のNa塩であり、下記
構造式を有しており、デンプン糊等で造粒した白色の水
溶性細粒状粉末である市販品として入手できる。
Sodium L-ascorbate is a Na salt of L-ascorbic acid generally known as vitamin C, has the following structural formula, and is a commercially available product that is a white water-soluble fine granular powder granulated with starch paste or the like. It is available as .

CH20)1 aO H このL−アスコルビン酸ナトリウムは、Lアスコルビン
酸と同様の強い抗酸化作用を有し、前記硫酸第1鉄に由
来する鉄(II)イオン(Fe2+)の酸化による鉄(
n)イオン(Fe3)の生成を阻止すると共に、Na塩
であることから処理剤全体としてのPHを高めて前記錯
体の形成反応を生じ易くする(PH3以下では錯体形成
が困難になる)ことにより、硫酸第1鉄による脱臭力と
その持続性を高める機能を果す。
CH20)1 aOH This sodium L-ascorbate has a strong antioxidant effect similar to that of L-ascorbic acid, and contains iron (II) ions (Fe2+) derived from the ferrous sulfate through oxidation.
n) In addition to preventing the generation of ions (Fe3), since it is a Na salt, it increases the pH of the treatment agent as a whole and facilitates the formation of the complex (complex formation becomes difficult at pH 3 or below). , functions to increase the deodorizing power and sustainability of ferrous sulfate.

また、一般に糞尿中には未消化食物等の酸化腐敗を生じ
るような様々な成分が含まれるが、本処理剤にて処理さ
れた糞尿は野外での貯溜中や施肥後においてもL−アス
コルビン酸ナトリウムによる抗酸化作用にて酸化腐敗を
生じにく\該腐敗による新たな悪臭発生も防止されるこ
とになる。
In addition, although manure and urine generally contain various components that cause oxidation and putrefaction, such as undigested food, manure treated with this treatment agent retains L-ascorbic acid even when stored outdoors or after fertilization. The antioxidant effect of sodium prevents oxidative putrefaction and also prevents the occurrence of new bad odors due to such putrefaction.

更に、この発明において重要な点は、L−アスコルビン
酸ナトリウムが土壌の酸性化を防止する機能を有し、本
処理剤にて処理された下肥の施肥によって格別なアルカ
リ化剤を用いずとも農作物の生育を向上させ得ることで
ある。これに対し、Na塩ではない単なるL−アスコル
ビン酸を用いた場合には、上記の酸性化の防止には効果
がなく、硫酸第1鉄の存在によって却って酸性化が促進
されるおそれがある。
Furthermore, an important point in this invention is that sodium L-ascorbate has the function of preventing soil acidification, and by fertilizing manure treated with this treatment agent, it can be done without using a special alkalizing agent. It is possible to improve the growth of agricultural crops. On the other hand, when simple L-ascorbic acid, which is not a Na salt, is used, it is not effective in preventing the above-mentioned acidification, and the presence of ferrous sulfate may actually accelerate acidification.

このようなL−アスコルビン酸ナトリウムの配合量は、
無水物(FeSO+)換算硫酸第1鉄に対して0.1〜
20重量%、特に好適には0.2〜5重量重量%上する
のが良く、少なすぎては上記の各作用共に不充分となり
、多すぎでは材料コスト上から不経済である。なお、前
記の鉄(II)イオンとアンモニアとの錯体を形成させ
る上で、処理剤添加混合後の処理液PHを3以上とする
必要があり、この点を考慮してL−アスコルビン酸ナト
リウムの上記配合量と処理剤の使用量を定めることが望
ましい。
The amount of sodium L-ascorbate is as follows:
0.1 to ferrous sulfate equivalent to anhydride (FeSO+)
The amount is preferably 20% by weight, particularly preferably 0.2 to 5% by weight; if it is too small, all of the above effects will be insufficient, and if it is too large, it will be uneconomical in terms of material cost. In addition, in order to form the above-mentioned complex between iron (II) ions and ammonia, the pH of the treatment solution after addition and mixing of the treatment agent needs to be 3 or more. It is desirable to determine the above blending amount and the amount of processing agent used.

フライアッシュは石炭ボイラーの煙道排ガス中から捕集
される微粉状の産業廃棄物であり、また天然ゼオライト
粉末は沸石として全国各地に大量に存在する鉱石の粉末
であり、共に安価に入手できる。しかして、前者のフラ
イアッシュは約1200℃の高温を経て無水状態である
が、後者の天然ゼオライト粉末は結晶中に多量の水分を
含んでいるため、加熱乾燥によって該水分をある程度除
去した形で使用することが推奨される。
Fly ash is a finely powdered industrial waste collected from the flue gas of coal boilers, and natural zeolite powder is an ore powder known as zeolite that exists in large quantities throughout the country, and both can be obtained at low cost. However, while the former fly ash becomes anhydrous after being heated to a high temperature of about 1200°C, the latter natural zeolite powder contains a large amount of water in its crystals, so it is dried by heating to remove some of the water. Recommended for use.

これらフライアッシュ及びゼオライト粉末は、硫酸第1
鉄による吸湿性を排除して処理剤粉末の吸湿塊状化を防
止すると共に、土壌に農作物の生育に必要な多種のミネ
ラル成分、例えばPlCa、Mg、KSsto2、A息
、B、Mo。
These fly ash and zeolite powder are
It eliminates the hygroscopicity caused by iron and prevents the processing agent powder from becoming hygroscopic and clumpy, and also contains various mineral components necessary for the growth of agricultural products in the soil, such as PlCa, Mg, KSto2, A breath, B, and Mo.

Mn SZn SSe等を供給する機能を果す。It functions to supply Mn, SZn, SSe, etc.

このようなフライアッシュ及びゼオライト粉末は、単独
で用いても良いし、両者を併用しても差し支えない。そ
の配合量は、無水物換算硫酸第1鉄に対して20〜10
0重量%、特に好適には25〜50重量%程度とするの
が良く、少なすぎては上記各作用が充分に発揮されず、
逆に多すぎては処理剤中の硫酸第1鉄成分の割合が相対
的に低下して処理に際して大量の処理0 剤を要することになる。
Such fly ash and zeolite powder may be used alone or in combination. The blending amount is 20 to 10% relative to ferrous sulfate in terms of anhydride.
It is preferable to set the amount to 0% by weight, particularly preferably about 25 to 50% by weight, and if the amount is too small, the above effects will not be fully exerted.
On the other hand, if the amount is too large, the proportion of the ferrous sulfate component in the treatment agent will be relatively reduced, and a large amount of treatment agent will be required for the treatment.

この発明の有機肥料化処理剤は、上述した硫酸第1鉄と
、L−アスコルビン酸ナトリウムと、フライアッシュま
たはゼオライト粉末とを単に混合した粉末混合物として
そのま\使用できるが、好適には該混合物を加熱乾燥し
て硫酸第1鉄の結晶水の一部を揮散させた形態とする。
The organic fertilizer treatment agent of the present invention can be used as it is as a powder mixture of the above-mentioned ferrous sulfate, sodium L-ascorbate, and fly ash or zeolite powder, but it is preferable to use the mixture as is. is heated and dried to form a form in which part of the crystal water of ferrous sulfate is volatilized.

すなわち、この結晶水の揮散により上記粉末混合物の吸
湿性が大きく低下するから、処理剤の保存安定性が向上
し、流動性が確保されて糞尿に対する添加混合が容易と
なる。
That is, the volatilization of this water of crystallization greatly reduces the hygroscopicity of the powder mixture, which improves the storage stability of the treatment agent, ensures fluidity, and facilitates addition and mixing with excrement.

有機肥料化処理を行うには、上述した処理剤を糞尿に添
加混合するだけでよい。この添加量は糞尿100投に対
して30〜200g程度であり、例えば200〜300
℃の便槽にはコツプ1〜2杯程度添加すればよい。
To carry out organic fertilizer processing, it is sufficient to simply add and mix the above-mentioned processing agent to manure. The amount added is about 30 to 200 g per 100 casts of excrement, for example, 200 to 300 g.
It is sufficient to add 1 to 2 tablespoons to the feces tank at ℃.

上記添加による脱臭作用は激烈であり、殆ど一瞬にして
糞尿特有の刺激的な悪臭が消え、これと共に糞尿が前記
反応によって黒く変色する。
The deodorizing effect caused by the above addition is intense, and the pungent odor peculiar to excrement disappears almost instantly, and at the same time, the excrement turns black due to the reaction.

しかして、−船釣に汲み取り後の糞尿は下肥と1 して施肥する前に長期間野外で放置して充分に発酵させ
る必要があるが、この発明の処理方法によれば処理後に
直ちに下肥として施肥することが可能となる。また、硫
酸第1鉄による脱臭効果が持続的に作用すると共にL−
アスコルビン酸ナトリウムによる酸化腐敗防止効果によ
り、下肥の野外貯溜中及び施肥後においても悪臭が発生
しない。
However, the manure collected by boat fishing must be left outdoors for a long period of time to fully ferment before being applied as manure, but according to the treatment method of the present invention, it must be immediately removed after treatment. It becomes possible to apply it as fertilizer. In addition, the deodorizing effect of ferrous sulfate acts continuously and L-
Due to the oxidative rot prevention effect of sodium ascorbate, no bad odor is generated even during field storage of manure and after fertilization.

一方、上記施肥により、下肥としての本来の肥料効果に
加えて、土壌に鉄分及び各種ミネラル分が供給され、且
つ土壌の酸性化が防止されることから、農作物の生育が
著く促進され、丈夫に大きく成長して高品位でしかも安
全な農作物を高収量で得ることができる。
On the other hand, by applying the above fertilizer, in addition to the original fertilizer effect as a bottom fertilizer, iron and various minerals are supplied to the soil, and acidification of the soil is prevented, so the growth of agricultural crops is significantly promoted. It grows strong and large, making it possible to obtain high-yield, high-quality, safe agricultural products.

なお、この発明の処理剤及び処理方法は、人の糞尿に限
らず家畜や家禽類の糞尿の有機肥料化にも同様に適用で
きるが、特に下肥とする人の糞尿に対する適用効果が大
である。
The treatment agent and treatment method of the present invention can be applied not only to human excrement but also to converting livestock and poultry excrement into organic fertilizer, but it is particularly effective when applied to human excrement, which is used as bottom manure. be.

実施例 以下、この発明を実施例により具体的に説明 2 する。Example Hereinafter, this invention will be specifically explained with examples 2 do.

実施例1 硫酸第1鉄7水塩(FeSO4・7H20)粉末100
重量部と、L−アスコルビン酸ナトリウム粉末(成田薬
品社製のビタミンCナトリウム顆粒99)3重量部と、
フライアッシュ50重量部とを混合した後、この混合物
を撹拌し80℃にて乾燥処理したのち粗砕して、粉末状
の有機肥料化処理剤を得た。
Example 1 Ferrous sulfate heptahydrate (FeSO4.7H20) powder 100
parts by weight, 3 parts by weight of sodium L-ascorbate powder (vitamin C sodium granules 99 manufactured by Narita Pharmaceutical Co., Ltd.),
After mixing with 50 parts by weight of fly ash, this mixture was stirred, dried at 80° C., and then crushed to obtain a powdered organic fertilizer treatment agent.

次に、この処理剤を糞尿かはV満杯になった200(便
槽に150g添加して混合したところ、直ちに悪臭が消
えて糞尿は黒く変色した。
Next, when 150 g of this treatment agent was added to a 200 (vacuum) tank full of excrement and urine and mixed, the foul odor immediately disappeared and the excrement turned black.

この処理後、糞尿を汲み出して下肥とする液状有機肥料
を得た。
After this treatment, the manure was pumped out to obtain a liquid organic fertilizer to be used as bottom manure.

実施例2 フライアッシュに代えて120℃にて30分間加熱乾燥
を行った天然ゼオライト粉末25重量部を使用し、実施
例1と同様にして有機肥料3 化処理剤を得た。次に、この処理剤を実施例1と同様の
便槽に添加混合したところ、直ちに悪臭が消えて糞尿は
黒く変色した。しかして、処理後の糞尿を汲み出して液
状有機肥料を得た。
Example 2 An organic fertilizer 3-conversion treatment agent was obtained in the same manner as in Example 1, except that 25 parts by weight of natural zeolite powder, which had been heated and dried at 120° C. for 30 minutes, was used instead of fly ash. Next, when this treatment agent was added and mixed into the same feces tank as in Example 1, the bad odor immediately disappeared and the feces and urine turned black. The treated manure was then pumped out to obtain liquid organic fertilizer.

実施例3 L−アスコルビン酸ナトリウム粉末の配合量を10重量
部、フライアッシュの配合量を100重量部に変更した
以外は実施例1と同様にして処理剤を得た。この処理剤
により実施例1と同様に糞尿の処理を行ったところ、実
施例1と同様の結果が得られた。
Example 3 A treatment agent was obtained in the same manner as in Example 1, except that the amount of sodium L-ascorbate powder was changed to 10 parts by weight, and the amount of fly ash was changed to 100 parts by weight. When this treatment agent was used to treat excreta in the same manner as in Example 1, the same results as in Example 1 were obtained.

比較例1 L−アスコルビン酸ナトリウム粉末を使用しなかった以
外は実施例1と同様にして得られた粉末混合物を処理剤
として、実施例1と同様に糞尿の処理を行った。
Comparative Example 1 Excrement and urine were treated in the same manner as in Example 1 using a powder mixture obtained in the same manner as in Example 1 as a treatment agent except that sodium L-ascorbate powder was not used.

4 比較例2 L−アスコルビン酸ナトリウム粉末の代わり1;L−ア
スコルビン酸粉末を同量使用した以外は実施例1と同様
にして得られた粉末混合物を処理剤として、実施例1と
同様に糞尿の処理を行った。
4 Comparative Example 2 Substitute for sodium L-ascorbate powder 1: Using a powder mixture obtained in the same manner as in Example 1 except that the same amount of L-ascorbic acid powder was used as a treatment agent, feces and urine were treated in the same manner as in Example 1. was processed.

以上の実施例及び比較例で得た液状有機肥料につき、便
槽からの汲み出し直後ならびに所定日数の野外放置後の
臭気の有無を調べたところ、下記第1表の結果が得られ
た。
The liquid organic fertilizers obtained in the above Examples and Comparative Examples were examined for the presence of odor immediately after being pumped out from the toilet tank and after being left outdoors for a predetermined number of days, and the results shown in Table 1 below were obtained.

第1表 5 次に、上記実施例及び比較例で得られた汲み取り直後の
液状有機肥料ならびに参考例1として未処理の糞尿を野
外で120日間放置して発酵させた下肥とを、それぞれ
中性質土壌を養土として、ITIt、当り4Qの割合で
施肥し、ホウレン草の種子を同数時いて発芽させ、以降
同一条件で生育させた。そして、発芽7日後に半分を収
穫し、残りを発芽21日後に収穫し、それぞれ1株当り
の平均重量を測定したところ、下記第2表の結果が得ら
れた。なお、表中の参考例2は施肥なしの同養土で生育
させたものである。
Table 1 5 Next, the liquid organic fertilizers immediately after pumping obtained in the above Examples and Comparative Examples and the manure prepared by fermenting untreated manure by leaving it outdoors for 120 days as Reference Example 1 were respectively added. Using the soil as nutrient soil, it was fertilized at a rate of 4Q per ITIt, and the same number of spinach seeds were planted and germinated, and thereafter grown under the same conditions. Then, half of the plants were harvested 7 days after germination, and the rest were harvested 21 days after germination, and the average weight of each plant was measured, and the results shown in Table 2 below were obtained. In addition, Reference Example 2 in the table was grown in nutrient soil without fertilization.

第2表 6 発明の効果 この発明の有機肥料化処理剤及び処理方法によれば、糞
尿を原料として、処理直後から施肥後に至るまで無臭で
且つ酸化腐敗を生じにく\、取扱い性に優れ、しかも糞
尿による肥料効果に加えて土壌を植物育成に最適な性状
及び組成とする液状有機肥料が提供される。しかして、
この液状有機肥料によれば、上記処理剤が材料的に安価
で且つ僅かな添加量で充分な処理が行えると共に糞尿自
体も原価がゼロに等しいことから、施肥コストが安くつ
き、しかも従来の下肥のように長期間の発酵を要さず処
理後に直ちに施肥でき、また悪臭を発生しないために周
辺環境を害さず、しかも施肥効率に優れて高収穫を達成
できるという数々の利点がある。従って、この発明は、
安全で高品位の農作物を得る有機農法の新たな発展に大
きく貢献できると共に、従来のし尿処理に要していた莫
大な費用の大幅な削減を可能にするものである。
Table 2 6 Effects of the Invention According to the organic fertilizer treatment agent and treatment method of the present invention, using manure as a raw material, it is odorless and resistant to oxidative rot from immediately after treatment to after fertilization, and has excellent handling properties. In addition, a liquid organic fertilizer is provided that not only provides the fertilizer effect of manure but also provides soil with properties and composition that are optimal for growing plants. However,
According to this liquid organic fertilizer, the above-mentioned treatment agent is inexpensive in terms of materials, sufficient treatment can be performed with a small amount added, and the cost of manure itself is equal to zero, so the cost of fertilization is low, and it is less expensive than conventional fertilizers. Unlike manure, it does not require long-term fermentation and can be applied immediately after treatment, and it does not harm the surrounding environment because it does not generate bad odors, and it has many advantages, such as being highly efficient in fertilization and achieving high yields. Therefore, this invention
This will not only greatly contribute to the new development of organic farming methods for producing safe, high-quality crops, but also make it possible to significantly reduce the enormous cost required for conventional human waste treatment.

なお、この発明の請求項(2)の有機肥料化7 処理剤では、各成分のそれぞれの作用が過不足なく発揮
されるという利点がある。また、この発明の請求項(4
)の有機肥料化処理方法によれば、完全に脱臭されて且
つ土壌へ充分な鉄分及びミネラル成分を供給し得る有機
肥料を確実に得ることができる。
The organic fertilizer treatment agent according to claim (2) of the present invention has the advantage that each component exhibits its respective effects in just the right amounts. In addition, claim (4) of this invention
According to the organic fertilizer processing method described in ), it is possible to reliably obtain an organic fertilizer that is completely deodorized and can supply sufficient iron and mineral components to the soil.

以上 8that's all 8

Claims (4)

【特許請求の範囲】[Claims] (1)硫酸第1鉄と、L−アスコルビン酸ナトリウムと
、フライアッシュまたはゼオライト粉末とを主成分とす
る糞尿の有機肥料化処理剤。
(1) A treatment agent for converting manure into organic fertilizer, the main components of which are ferrous sulfate, sodium L-ascorbate, and fly ash or zeolite powder.
(2)無水物(FeSO_4)換算硫酸第1鉄に対して
、L−アスコルビン酸ナトリウムが0.1〜20重量%
、フライアッシュまたはゼオライト粉末が20〜100
重量%、それぞれ配合されてなる請求項(1)記載の糞
尿の有機肥料化処理剤。
(2) Sodium L-ascorbate is 0.1 to 20% by weight based on ferrous sulfate in terms of anhydride (FeSO_4)
, fly ash or zeolite powder from 20 to 100
The treatment agent for converting manure into organic fertilizer according to claim (1), wherein the respective amounts are blended in weight%.
(3)硫酸第1鉄と、L−アスコルビン酸ナトリウムと
、フライアッシュまたはゼオライト粉末とを主成分とす
る処理剤を糞尿に添加混合することを特徴とする糞尿の
有機肥料化処理方法。
(3) A method for processing manure into organic fertilizer, which comprises adding and mixing to manure a treatment agent containing ferrous sulfate, sodium L-ascorbate, and fly ash or zeolite powder as main components.
(4)処理剤の添加量が糞尿100lに対して30〜2
00gの範囲である請求項(3)記載の糞尿の有機肥料
化処理方法。
(4) The amount of processing agent added is 30 to 2 per 100 liters of excrement.
The method for converting manure into organic fertilizer according to claim 3, wherein the amount is in the range of 0.00 g.
JP1263581A 1989-10-09 1989-10-09 Manure organic fertilizer treatment agent and treatment method Expired - Lifetime JP2619073B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1263581A JP2619073B2 (en) 1989-10-09 1989-10-09 Manure organic fertilizer treatment agent and treatment method

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Application Number Priority Date Filing Date Title
JP1263581A JP2619073B2 (en) 1989-10-09 1989-10-09 Manure organic fertilizer treatment agent and treatment method

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JPH03126688A true JPH03126688A (en) 1991-05-29
JP2619073B2 JP2619073B2 (en) 1997-06-11

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Country Link
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2003008517A1 (en) * 2001-07-19 2003-01-30 Columbus Corporation Co., Ltd. Composition for soil containing industrial waste as primary component
JP2006345738A (en) * 2005-06-14 2006-12-28 Nippon Steel Corp Fertilizer material and fertilizing method

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6143091A (en) * 1984-08-03 1986-03-01 Hamamatsu Photonics Kk Stereoscopic television device
JPS6296046A (en) * 1985-10-19 1987-05-02 Minato Sangyo Kk Feed additive and its production
JPS62123026A (en) * 1985-11-25 1987-06-04 Nippon Zeon Co Ltd Powdery composition containing iron compound
JPS63185881A (en) * 1987-01-29 1988-08-01 大成建設株式会社 Manufacture of compost

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6143091A (en) * 1984-08-03 1986-03-01 Hamamatsu Photonics Kk Stereoscopic television device
JPS6296046A (en) * 1985-10-19 1987-05-02 Minato Sangyo Kk Feed additive and its production
JPS62123026A (en) * 1985-11-25 1987-06-04 Nippon Zeon Co Ltd Powdery composition containing iron compound
JPS63185881A (en) * 1987-01-29 1988-08-01 大成建設株式会社 Manufacture of compost

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2003008517A1 (en) * 2001-07-19 2003-01-30 Columbus Corporation Co., Ltd. Composition for soil containing industrial waste as primary component
JP2003096452A (en) * 2001-07-19 2003-04-03 Soruteko Kk Composition for soil consisting of industrial waste
JP2006345738A (en) * 2005-06-14 2006-12-28 Nippon Steel Corp Fertilizer material and fertilizing method
JP4616087B2 (en) * 2005-06-14 2011-01-19 新日本製鐵株式会社 Fertilizing material and fertilizing method

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