JPS61141689A - Method of removing bad smell and manufacturing humus acid simultaneously - Google Patents

Method of removing bad smell and manufacturing humus acid simultaneously

Info

Publication number
JPS61141689A
JPS61141689A JP59264146A JP26414684A JPS61141689A JP S61141689 A JPS61141689 A JP S61141689A JP 59264146 A JP59264146 A JP 59264146A JP 26414684 A JP26414684 A JP 26414684A JP S61141689 A JPS61141689 A JP S61141689A
Authority
JP
Japan
Prior art keywords
raw material
mixture
feces
additive
additives
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
JP59264146A
Other languages
Japanese (ja)
Other versions
JPH0535117B2 (en
Inventor
敏 井上
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP59264146A priority Critical patent/JPS61141689A/en
Publication of JPS61141689A publication Critical patent/JPS61141689A/en
Publication of JPH0535117B2 publication Critical patent/JPH0535117B2/ja
Granted 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

Landscapes

  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Fertilizers (AREA)

Abstract

(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。
(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 〔発明の分野〕 本発明は畜糞、人糞などの排泄物の悪臭を除去しながら
、同時にこれら排泄物を原料として土壌改良に有益な腐
植酸を人工的に製造する方法に関する。
[Detailed Description of the Invention] [Field of the Invention] The present invention removes the bad odor of excrement such as animal feces and human feces, while at the same time artificially producing humic acid useful for soil improvement using these excrements as raw materials. Regarding the method.

〔背景技術〕[Background technology]

作物は無機物を養分として有機物を作り、有機物である
作物は動物に利用された後、微生物によって無機化され
、再び作物の養分として吸収される。この自然界のサイ
クルによって農業の連続性が保たれる。
Crops use inorganic matter as nutrients to create organic matter, and after the organic matter is used by animals, it is mineralized by microorganisms and absorbed again as nutrients by the crops. This natural cycle maintains the continuity of agriculture.

しかるに、近年、農業の生産性を高めるために作物農家
と畜産農家の分離、専業化が進んだ結果、本来あるべき
自然のサイクルが断たれ、いくつかの重大な弊害を生む
に至っている。
However, in recent years, as a result of the separation and specialization of crop farmers and livestock farmers in order to increase agricultural productivity, the natural cycle that should exist has been disrupted, resulting in several serious adverse effects.

一つは蓄産から生ずる大量の排泄物の問題である。すな
わち、畜産農家にあっては機械化、大規模化により畜糞
などの大量の排泄物が発生する。
One is the problem of large amounts of excrement generated from livestock farming. In other words, livestock farms generate large amounts of excrement such as livestock manure due to mechanization and larger scale farming.

これら家畜の排泄物は今や年間平均的5,6007tに
達し、そのうち肥料として利用されているのは6〜7万
t (0,001%程度)にすぎず残りは山野に投棄さ
れている。このため、近隣に悪臭公害と河川及び湖沼の
汚染公害をもたらし、蓄産の経営自体が危機にさらされ
ているのが現状である。
The average amount of excrement from these livestock has now reached 5,6007 tons per year, of which only 60,000 to 70,000 tons (approximately 0,001%) is used as fertilizer, and the rest is dumped in the mountains and fields. As a result, the current situation is that the management of the farm itself is under threat, causing odor pollution in the vicinity and contamination of rivers and lakes.

他方、作物農家にあっては化学肥料の多用に伴い地力の
根源である有機物の不足による土壌の疲弊が進み、ひい
ては表土流出という世界的な問題をひきおこしている。
On the other hand, for crop farmers, the heavy use of chemical fertilizers is leading to soil depletion due to a lack of organic matter, which is the root of soil fertility, and this is causing the global problem of topsoil runoff.

これらの問題を解決するべく種々の畜糞肥料化処理方法
が知られているが、下記のような欠点があり、満足を得
るものがない。
Various livestock manure fertilizer processing methods are known to solve these problems, but none of them are satisfactory due to the following drawbacks.

すなわち、天日、重油(火力)等で畜糞等を乾燥して肥
料化する乾燥式処理方法は処理中に耐え難い悪臭が発生
する。特に重油乾燥式は悪臭が著しいため現在ではほと
んど採用されていない。また、天日乾燥式は悪臭公害も
さることながら、大量処理ができない上、天候や季節に
影響されるため商品化は困難であり自家消費程度にしか
利用されていない。しかもこれら乾燥式処理方法はいず
れも肥料化された製品が水分を含むと元の糞に戻ってし
まうという難点がある。
That is, the dry processing method, in which animal manure is dried under the sun, heavy oil (firepower), etc. and turned into fertilizer, produces an intolerable odor during processing. In particular, the heavy oil drying method is rarely used at present because of its pronounced odor. In addition, the solar drying method not only causes odor pollution but also cannot process large quantities and is affected by the weather and season, making it difficult to commercialize and is only used for home consumption. Moreover, all of these dry processing methods have the disadvantage that when the fertilizer product contains moisture, it returns to its original form.

このため、今日では畜糞等を発酵させて肥料化する発酵
処理方法が主流となっているが、この方式は処理に30
日乃至120日、平均60日を要し、大きな場所を要す
る割に1日当りの処理量が限られる#1か、発酵処理中
に長期間にわたって悪臭が発生し続けるため新たな公害
をひきおこしている。また、完全発酵が困難なため肥料
化した場合の製品にムラがあり、且つ二次発酵によシ悪
臭が発生するため商品化が困難であった。
For this reason, the fermentation treatment method that ferments animal dung and other materials to turn it into fertilizer has become mainstream today, but this method requires 30% of the processing time.
It takes 120 days on average, 60 days on average, and the amount of processing per day is limited due to the large space required.Also, the bad odor continues to be generated for a long period of time during the fermentation process, causing new pollution. . Furthermore, since complete fermentation is difficult, the product produced as fertilizer is uneven, and secondary fermentation generates a bad odor, making commercialization difficult.

このように、従来の畜糞処理方法には処理中及び処理後
の悪臭と処理時間に問題があるほかさらに土壌の肥沃化
という点で以下のような重大な欠点がある。すなわち、
乾燥式、発酵式のいずれも畜糞をそのまま堆肥化するに
すぎないため早期に完全分解してしまい地力の根源であ
る腐植物質を生成しない。従って、肥料としての機能は
あるけれども地力強化としての土壌改良にはなり得ない
のである。
As described above, the conventional livestock manure treatment method has problems with the bad odor during and after treatment and the treatment time, and also has the following serious drawbacks in terms of soil fertilization. That is,
Both the dry method and the fermentation method simply compost livestock manure, so it completely decomposes quickly and does not produce humic substances, which are the source of soil fertility. Therefore, although it has a function as a fertilizer, it cannot be used as a soil improvement agent to strengthen soil fertility.

尚、畜糞にオガクズを混合して発酵させる処理方法が知
られているが混合物中の畜糞が早期に分解するのに対し
、オガクズは容易に分解しないため土壌改良の機能を有
しないだけでなく、オガクズだけが未分解のまま土壌中
に層状の障害物として残る弊害がある。
Incidentally, a treatment method is known in which sawdust is mixed with livestock manure and fermented, but while the livestock manure in the mixture decomposes quickly, sawdust does not decompose easily, so it not only does not have the function of soil improvement. Only sawdust has the disadvantage of remaining undecomposed in the soil as a layered obstruction.

〔発明の目的〕[Purpose of the invention]

以上の問題に鑑み、本発明の目的は畜糞、人糞等の排泄
物から発生する悪臭を除去しながらこれら排泄物を原料
として土壌改良に有益な腐植酸を人工的に生成すること
により畜糞による悪臭公害と有機物の不足による土壌疲
弊を同時に解決することにある。
In view of the above problems, the purpose of the present invention is to remove the bad odor generated from excrements such as livestock feces and human feces, and to artificially generate humic acid useful for soil improvement using these excrements as raw materials. The aim is to simultaneously solve the problem of odor pollution and soil exhaustion due to lack of organic matter.

本発明の他の目的は自然物に近い腐植酸を短期間に人工
的に生成することにある。
Another object of the present invention is to artificially produce humic acid close to natural products in a short period of time.

本発明のさらに他の目的は、原料及び添加物の水分含有
量に対し、製品ムラのない人工腐植酸の製造方法を提供
することにある。
Still another object of the present invention is to provide a method for producing artificial humic acid with uniformity in the water content of raw materials and additives.

〔発明の概要〕[Summary of the invention]

本発明者は大量に発生する畜糞から悪臭等の公害をなく
し、有効な肥料を作り出すべく種々研究を重ねた結果、
畜糞、人糞など覧原料とし、この原料にミズゴケ泥炭ま
たはミズゴケ泥炭とりゲニンスルホン酸を添加物として
混合し、この混合物を反応槽において少なくとも60℃
以、上に加圧混練するとともに、混練した混合物の少な
くとも一部を乾燥させた後加圧混練前の原料糞と添加物
の混合物に循環混合して再度前記加圧混練を反復する工
程を少なくとも一回施すことにより腐植酸を短時間に人
工的に製造することができたものである。
The inventor of the present invention has conducted various researches in order to eliminate pollution such as bad odors from large amounts of livestock manure and create an effective fertilizer.
Animal excrement, human excrement, etc. are used as raw materials, sphagnum peat or sphagnum peat and geninsulfonic acid are mixed as an additive to this raw material, and this mixture is heated at at least 60°C in a reaction tank.
Above, at least the step of pressurized kneading, drying at least a part of the kneaded mixture, circulation mixing into the mixture of raw material excrement and additives before pressurized kneading, and repeating the pressurized kneading again. Humic acid can be artificially produced in a short time by applying it once.

〔発明の実施例〕[Embodiments of the invention]

有機物と微生物によって土壌中で長期間をかけて生成さ
れる天然の土壌腐植酸はその化学構造が一様ではないも
のの構成成分の50%はアミノ酸、グリコサミン、芳香
族化合物及び官能基からなる暗色の物質である。
Natural soil humic acid, which is produced over long periods in the soil by organic matter and microorganisms, has a variable chemical structure, but 50% of its constituents are dark-colored, consisting of amino acids, glycosamines, aromatic compounds, and functional groups. It is a substance.

このうち、アミノ酸、グリコサミンの組成は微生物に特
異的に含まれているアミノ酸及びアミノ糖の含有濃度が
きわめて高く、これは微生物の遺体によるものである。
Among these, the composition of amino acids and glycosamines has extremely high concentrations of amino acids and amino sugars that are specifically contained in microorganisms, and this is due to the remains of the microorganisms.

また、芳香族化合物は微生物によって分解されにくいリ
グニンを主体とし、他の有機物や微生物の中間代謝産物
から構成されている。
In addition, aromatic compounds are mainly composed of lignin, which is difficult to be decomposed by microorganisms, and are composed of other organic substances and intermediate metabolites of microorganisms.

すなわち、腐植物は動植物、微生物遺体および微生物の
中間代謝産物に由来する芳香族化合物が炭水化物の関与
のもとにタン・ぐり質やにブタイド化合物と重縮合をく
り返して生成された酸性で暗色の高分子物質であること
が知られている。
In other words, humus is an acidic, dark-colored compound produced by repeated polycondensation of aromatic compounds derived from plants and animals, microbial remains, and intermediate metabolites of microorganisms with butide compounds in the presence of carbohydrates. It is known to be a polymeric substance.

本発明の特徴は人及び鶏、豚、牛などの電蓄の排泄物(
以下畜糞という)を原料とし、これにミズゴケ泥炭を主
材とする添加物−一@混合した後加圧混練するとともに
、混線後の反応生成物少なくとも一部を乾燥させた後、
加圧混練前の原料糞と前記添加物の混合物に混合し、こ
れをさらに加圧混練して腐植酸を製造することにある。
The feature of the present invention is that electricity storage excreta (human, chicken, pig, cow, etc.)
(hereinafter referred to as livestock dung) is used as a raw material, and an additive mainly composed of sphagnum moss peat is mixed therewith and then kneaded under pressure. After drying at least a part of the reaction product after mixing,
The purpose is to mix the raw material feces before kneading under pressure with a mixture of the additives and further knead them under pressure to produce humic acid.

■ 一般に1鶏、豚などの畜糞及び人糞は(1)その−の景
を占める各種の腸内菌及び未消化物からなる蛋白ff、
(2)セルロース、ヘミセルロース、!澱粉などの炭水
化物43)リグニン、及び(4)アミノ糖類である腸内
粘質物、などの有機成分を含んでいる。これらの畜糞は
易分解性のためそのままでは土壌中で完全分解し易く腐
植となりにくいものである。このため本発明は第1図に
示すようにまず第一工程として原料である畜糞に可溶性
炭水化物、ヘミセルロース及びキノン系物質の含有量が
多い下等植物であるところのミズゴケ泥炭を主成分とす
る添加物を混入し充分に混合する。   −ここでミズ
ゴケ泥炭とは上層のミズゴケ部分と下層の泥炭化したミ
ズゴケを総称し、いずれをも意味する趣旨である。
■ In general, animal excrement from chickens, pigs, etc. and human excrement contain (1) protein ff, which is made up of various intestinal bacteria and undigested matter,
(2) Cellulose, hemicellulose,! It contains organic components such as carbohydrates such as starch, (4) lignin, and (4) intestinal mucilage, which is an amino sugar. Since these animal manures are easily decomposed, they are easily completely decomposed in the soil and are difficult to turn into humus. Therefore, as shown in Figure 1, the present invention involves the addition of sphagnum peat, which is a lower plant material containing a large amount of soluble carbohydrates, hemicellulose, and quinone-based substances, as a main component to livestock manure as a raw material. Add the ingredients and mix thoroughly. - Here, sphagnum peat is a general term for the upper layer of sphagnum moss and the lower layer of sphagnum moss that has turned into peat, and is intended to mean both.

添加物はミズゴケ泥炭単独かあるいはミズゴケ泥炭を主
成分としてこれにリグニンスルホ/酸ヲ混合(例えばミ
ズゴケ泥炭70重量%に対しりグ二/スルホン酸30重
量%)したものを用いる。
As the additive, sphagnum peat alone or a mixture of sphagnum peat and lignin sulfonic acid/acid (for example, sphagnum peat 70% by weight to lignin/sulfonic acid 30% by weight) is used.

すなわち、製品としての腐植酸に含まれるリグニンは土
壌中における腐植酸の急激な分解を抑制して長期にわた
る土壌改良効果を上げるとともに、土壌の団粒構造化を
促進する上で重要であるが、原料糞は牛糞で約29.8
%、豚糞で約13.8%、鶏糞で約8,5チのリグニン
を含んでおシ、またミズゴケ泥炭自体にも少量ながらリ
グニンが含まれているので、原料糞のりグニ/含有量が
多い場合、あるいは比較的分解の早い腐植酸を得たい場
合はミズゴケ泥炭のみを添加物として混合すれば足シ、
他方リグニン含有量の少ない原料糞を使用する場合や分
解の遅い腐植酸を製造する場合の添加物はミズゴケ泥炭
を主体としそのほかにリグニンスルホン酸を加えるのが
有利である。
In other words, the lignin contained in humic acid as a product is important in suppressing the rapid decomposition of humic acid in the soil, increasing the long-term soil improvement effect, and promoting the formation of aggregate structures in the soil. The raw material is cow dung, which is approximately 29.8
%, pig manure contains about 13.8%, chicken manure contains about 8.5% lignin, and sphagnum peat itself also contains a small amount of lignin. If there is a lot of humic acid, or if you want to obtain humic acid that decomposes relatively quickly, you can add only sphagnum peat as an additive.
On the other hand, when using raw material manure with a low lignin content or when producing humic acid which decomposes slowly, it is advantageous to use sphagnum peat as the main additive, with the addition of lignin sulfonic acid.

これら添加物はりゲニン成分を除き比較的分解し易いの
でそのまま使用することもできるが、次の反応工程にお
ける原料糞との反応分解条件の差添加物の上記酸処理は
反応促進効果を上げるだけでなく使用する酸く応じてア
ンモニアを硝酸アンモニアあるいは硫酸アンモニア等に
固定する作用があシ、さらには原料糞の脱臭作用にも有
利に働く。
Since these additives are relatively easy to decompose except for the aurigenin component, they can be used as they are, but there is a difference in the reaction decomposition conditions with the raw material feces in the next reaction process.The above acid treatment of the additives only increases the reaction promotion effect. Depending on the acidity used, it has the effect of fixing ammonia into ammonia nitrate or ammonia sulfate, and is also advantageous in deodorizing raw material feces.

原料糞に対する添加物の混合比率は重量比で2〜60%
が実施可能の範囲であるが反応速度、製品の品質等から
10〜30%程度とするのが望ましい。
The mixing ratio of additives to raw material feces is 2 to 60% by weight.
is within a practicable range, but it is preferably about 10 to 30% from the viewpoint of reaction rate, product quality, etc.

このように原料糞に前記添加物を混合することにより反
応の前工程と原料糞の脱臭処理が同時になされるととK
なる。
In this way, by mixing the additives into the raw material feces, the pre-reaction step and the deodorizing treatment of the raw material feces can be performed at the same time.
Become.

すなわち、畜糞の悪臭の成分は主としてアンモニア、メ
チルカプタン、硫化水素、トリメチルアミン、二硫化メ
チル等であるが、これらは(1)添加物のりゲニンの官
能基との反応、(2)酸処理で与えられた酸による反応
分解、(3)ミズゴケ泥炭による臭いの吸着、並びに(
4)ミズゴケ泥炭から溶出される有機酸、キノン類との
反応などにより効果的に脱臭される。このことは、原料
糞に前記添加物を混合した時点ですでに悪臭がなくなる
ことを意味いた点に鑑みると、本発明の上記工程は悪臭
公害を防止する上できわめて意義が深い。
In other words, the components that give off the bad odor of livestock manure are mainly ammonia, methylcaptan, hydrogen sulfide, trimethylamine, methyl disulfide, etc., which are produced by (1) reaction with the functional group of the additive rigenin, and (2) acid treatment. (3) odor adsorption by sphagnum peat;
4) It is effectively deodorized by reactions with organic acids and quinones eluted from sphagnum peat. Considering that this means that the bad odor is already gone at the time when the additive is mixed with the raw material feces, the above-mentioned process of the present invention is extremely significant in preventing bad odor pollution.

次に、原料光と添加物を充分に混ぜ合せた混合物を反応
槽において加圧混練しながら60℃以上、好ましくは8
0℃前後の高温下で分解及び反応させる。
Next, the mixture of raw material light and additives is thoroughly mixed in a reaction tank while being kneaded under pressure at 60°C or higher, preferably at 80°C.
Decompose and react at high temperatures around 0°C.

このように原料光と添加物の混合物を高温高圧の条件下
で混練することにより、糞の腸内菌蛋白、未消化蛋白、
腸内粘質物のアミノ糖類等が分解するとともKこれら分
解生成物と、原料光及び添加物中の変成リグニン及び/
またはミズゴケ泥炭に含まれているキノン系物質及び可
溶性炭水化物の分解物とがそれぞれ反応し、主として、
(1)  IJゲニンとアミノ酸の複合体及び分解の浅
い場合はタン・ぐりとの複合体 (2)  キノン系物質とアミノ酸化合物(3)炭水化
物分解物とアミノ酸化合物などが生成される。同時に、
加圧混練の際に他の少量含有物も分解及び重縮合を複雑
多様にくり返す。
By kneading the mixture of raw material light and additives under high temperature and high pressure conditions, we can produce fecal intestinal bacteria protein, undigested protein,
When amino sugars etc. in intestinal mucus are decomposed, these decomposition products and modified lignin and/or in raw materials and additives are
Or, quinone-based substances and decomposition products of soluble carbohydrates contained in sphagnum peat react with each other, and mainly,
(1) A complex of IJ genin and amino acids and, if the decomposition is shallow, a complex with tongue/grip (2) Quinone substances and amino acid compounds (3) Carbohydrate decomposition products and amino acid compounds are produced. at the same time,
During pressurized kneading, other substances contained in small amounts also undergo decomposition and polycondensation in a complex manner.

次いで、このように原料光と添加物の混合物を加圧混練
により分解反応させた生成物の少なくとも一部を充分に
乾燥することにより未分解の腸内菌及びその細胞壁を分
解し易くした後、これを原料光と添加物の未反応混合物
に混入させ前記の加圧混線を反復する。乾燥及び混入に
供する量は反応の進行度合及び原料光等の水分含有率に
よって必ずしも一定ではないが、通常は加圧混練された
←峰→4生成品の約50%を循環させることができる。
Next, at least a portion of the product obtained by subjecting the mixture of raw material light and additives to a decomposition reaction by pressure kneading is sufficiently dried to make it easier to decompose undecomposed intestinal bacteria and their cell walls. This is mixed into the unreacted mixture of raw material light and additives, and the above-mentioned pressurized mixture is repeated. Although the amount used for drying and mixing is not necessarily constant depending on the progress of the reaction and the water content of the raw materials, it is usually possible to circulate about 50% of the pressure-kneaded ←mine→4 product.

より好ましい実施として、加圧混練前の原料光と添加物
の混合物の水分を検出し、検出値に応じて混入量を調整
することも可能である。
As a more preferable implementation, it is also possible to detect the water content of the mixture of raw material light and additives before pressurized kneading, and adjust the amount of mixture in accordance with the detected value.

加圧混線、ずみの生成品の一部を乾燥させて未反応の混
合物と共に反復して加圧混練する上記工程  □を便宜
的に乾燥反復工程と呼ぶことにする。かかる乾燥反復工
程を設ける理由及び利点は以下の通りである。
For convenience, the step □ of drying a part of the resulting product and repeatedly pressurizing and kneading it with the unreacted mixture will be referred to as the repeated drying step. The reasons and advantages of providing such repeated drying steps are as follows.

すなわち、原料光の約1/3は腸内微生物であるがこれ
らの腸内菌は他の含有物に比べ細菌特有の細胞壁構造の
為に分解しにくく、従って一回の加圧混線では所望程度
に分解反応の進んだ腐植酸を得にくい。
In other words, approximately 1/3 of the raw material light is intestinal microorganisms, but these intestinal bacteria are difficult to decompose compared to other substances due to their unique cell wall structure. It is difficult to obtain humic acid, which undergoes an advanced decomposition reaction.

また−回だけの加圧混練では反応進行度が一様なため自
然界の土壌腐植酸のように重縮合の程度がさまざまで構
造不均一な物質との間に開きがあり、さらには原料光の
水分含有量によって生成腐植酸の品質にムラが生ずると
いう問題がある。
In addition, because the rate of reaction progress is uniform in pressurized kneading only once, there is a difference in the degree of polycondensation and structural non-uniform substances such as soil humic acid in the natural world. There is a problem in that the quality of the produced humic acid varies depending on the water content.

本発明では前記の乾燥反復工程を径ることによりこれら
の問題を同時に解決することができる。
In the present invention, these problems can be solved simultaneously by carrying out the drying process described above.

従って本発明は該乾燥反復工程を必ずしも一回に限定せ
ず、必要に応じて数回くり返す場合を含むものである。
Therefore, the present invention does not necessarily limit the drying process to one time, but includes cases where the drying process is repeated several times as necessary.

以上のように、原料光と添加物の混合工程、混合物の加
圧混線工程及び−次または数次の乾燥反復工程を順次経
過することにより暗色の腐植酸が生成されろ。
As described above, dark-colored humic acid is produced by sequentially performing the mixing process of raw material light and additives, the pressurizing and mixing process of the mixture, and the drying process of one or several times.

本発明の方法による腐植酸の製造は以下に述べる一連の
装置によって短時間に大量生産が可能である。以下に第
2乃至第4図を参照して洋間する。
Humic acid can be produced in large quantities in a short period of time by the method of the present invention using a series of apparatuses described below. The Western-style room will be explained below with reference to FIGS. 2 to 4.

原料光は原料光タンク1からモータ2で作動する二軸ス
クリュ3で混練されなから給送Aイブ4を介して混合機
5の投入口6から混合機5内に送られる。他方ミズゴケ
泥炭またはミズゴケ泥炭とりゲニンスルホン酸の混合物
からなる添加物は、必要に応じて酸処理された後、添加
物タンク7からベルトフィーダ8を介して混合機50投
入口6から混合機5内に供給される。かくして原料光と
添加物は混合機5内で合流され、モータ9で作動するス
クリs−一式混合機5で混合と脱臭処理を同時に行いな
がら出口側5′へ押しやられる。
The raw material light is kneaded by a twin screw 3 operated by a motor 2 from a raw material light tank 1, and then sent into the mixer 5 from an input port 6 of the mixer 5 via a feeding A-build 4. On the other hand, the additive consisting of sphagnum peat or a mixture of sphagnum peat and geninsulfonic acid is fed into the mixer 5 from the additive tank 7 via the belt feeder 8 from the input port 6 of the mixer 50, after being acid-treated as necessary. supplied to In this way, the raw material light and the additives are combined in the mixer 5, and are pushed to the outlet side 5' while simultaneously performing mixing and deodorizing treatment in the scrubber mixer 5 operated by the motor 9.

混合機5の出口側5′は二軸式連続加圧混練機11と・
母イブ10を介して連通しているとともにこの・ぐイブ
10にはモータ12で作動する送シ出し装置12′が介
装され、原料光と添加物の混合物を前記加圧混線機11
に導入するようになっている。
The outlet side 5' of the mixer 5 is connected to a twin-screw continuous pressure kneader 11.
A feeding device 12' operated by a motor 12 is interposed in the mother tube 10 and communicates with the mother tube 10.
It is planned to be introduced in

加圧混線機11の内部軸方向には、第4図に示すように
後方にスクリュl1mを有し且つ前方に複数の攪拌翼1
1bを固設した一対の軸11C911cが平行に枢着さ
れ、モータ13によ多回転するように組付けられている
In the internal axial direction of the pressurized mixer 11, as shown in FIG.
A pair of shafts 11C911c to which 1b is fixedly mounted are pivoted in parallel and assembled to the motor 13 so as to rotate multiple times.

かくして原料糞と添加物の混合物は加圧混練機11にお
いてスクリュ111Lで加圧され、攪拌翼11bによっ
て混線及び1*1r されることにより少なくとも60
℃以上、好ましくは80℃前後に昇温され、この高温高
圧下において前記分解及び反応が行われる。尚、14は
温度検出機である。
In this way, the mixture of raw material feces and additives is pressurized by the screw 111L in the pressurized kneader 11, mixed with the stirring blade 11b and mixed by 1*1r, so that at least 60
The temperature is raised to above .degree. C., preferably around 80.degree. C., and the decomposition and reaction are carried out at this high temperature and high pressure. Note that 14 is a temperature detector.

加圧混線機11は後端側に内部の、生成物を製品として
取出すためのスクリュコンペアなどの製品取出装置15
と乾燥機16に連絡するベルトコンベアなどの搬送手段
17を備えているとともにこれら製品取出装置15と搬
送手段17へ内部生成物を選択的にあるいは所望割合で
同時に送り出すための排出制御装置18を有している。
The pressurized mixer 11 has an internal product take-out device 15 such as a screw comparator for taking out the product as a product on the rear end side.
and a conveying means 17 such as a belt conveyor that communicates with the dryer 16 and a discharge control device 18 for selectively or simultaneously conveying internal products to the product take-out device 15 and the conveying means 17 in a desired ratio. are doing.

乾燥機16は一端側すなわち上流側が前記搬送手段17
を介して前記加圧混線機11の内部に連絡し、他端側す
なわち下流側はベルトフィーダなどの供給装置19と投
入口20を介して前記混合機5の内部に連絡するように
設置されている。従って加圧混練機11の前記搬送手段
17から送り出された反応生成物は乾燥機16によって
所望の乾燥度で乾燥された後、混合I@5に循環され、
混合機5内に供給されて来る後続の原料糞と添加物の混
合物と混ぜ合わされた後、再び加圧混線機11において
高温加圧下で混練され、分解、反応をくり返す。
The dryer 16 has one end side, that is, the upstream side, connected to the conveying means 17.
The other end side, that is, the downstream side, is installed so as to communicate with the inside of the mixer 5 via a supply device 19 such as a belt feeder and an input port 20. There is. Therefore, the reaction product sent out from the conveying means 17 of the pressure kneading machine 11 is dried to a desired degree of dryness by the dryer 16, and then circulated to the mixing I@5.
After being mixed with the subsequent mixture of raw material feces and additives supplied into the mixer 5, it is again kneaded in the pressure mixer 11 under high temperature and pressure, and the decomposition and reaction are repeated.

以上の工程をくシ返した後加圧混線機11内の反応生成
物が所望構造の腐植酸に生成された時点でこれを製品取
出装置15から排出させ、粉体あるいは(レッ)K成形
して袋詰めをする。尚、製品取出しは乾燥機16への循
環を維持しながら行うことはもちろん可能であり、一連
の工程を休みなく連続運転することができる。
After repeating the above steps, when the reaction product in the pressurized mixer 11 is formed into humic acid with the desired structure, it is discharged from the product take-out device 15 and molded into powder or K-molded. and pack it into bags. Incidentally, it is of course possible to take out the product while maintaining circulation to the dryer 16, and the series of steps can be continuously operated without interruption.

尚、所望により、混合機5に内部混合物の水分含有率を
検出するセンサ21を取付け、該センサ21の出力信号
により乾燥機16と混合機5間の供給装置19の供給量
をコントロールし、これにより混合機5内の混合物の水
分に応じて混合機5への乾燥生成物の混入量を調節する
ように構成することかできる。このように構成する場合
は原料糞の水分に変動があっても生成される腐植酸の水
分を自動的に一定に保ち、製品の均質化を計ることがで
きる。
If desired, a sensor 21 for detecting the moisture content of the internal mixture is attached to the mixer 5, and the output signal of the sensor 21 controls the supply amount of the supply device 19 between the dryer 16 and the mixer 5. Accordingly, the amount of the dry product mixed into the mixer 5 can be adjusted depending on the moisture content of the mixture in the mixer 5. With this configuration, even if the moisture content of the raw material feces varies, the moisture content of the humic acid produced can be automatically kept constant, thereby making it possible to homogenize the product.

尚、本発明方法を上記装置で実施する場合の原料投入か
ら製品取出しまでの所要時間は約40分である。
Incidentally, when the method of the present invention is carried out using the above-mentioned apparatus, the time required from inputting the raw materials to taking out the product is approximately 40 minutes.

〔発明の効果〕〔Effect of the invention〕

以上のように本発明の方法は原料蓄糞の悪臭を除去しな
がら有機質肥料として有用な腐植酸を短時間で量産でき
るので悪臭公害の防止と土壌改良を同時に達成すること
ができる。特忙処理の初期工程からすでに悪臭がなくな
るので作業者及び処理場所の確保が容易となり、利用度
が拡大する。
As described above, the method of the present invention can mass-produce humic acid useful as an organic fertilizer in a short time while removing the bad odor of raw material accumulated feces, and thus can simultaneously achieve prevention of bad odor pollution and soil improvement. Since bad odors are already eliminated from the initial process of special processing, it becomes easier to secure workers and processing areas, increasing the number of uses.

従って蓄光の放置がなくなるから悪臭公害や汚染公害の
防止に大きく寄与できる。
Therefore, since there is no need to leave phosphorescence unattended, it can greatly contribute to the prevention of foul odor pollution and pollution.

さらに、生成品の一部をく9返し分解、反応させて混合
するので製品としての腐植酸は分解、反応の進んだもの
から浅いものまで種々雑多な成分で構成されることにな
る。従って、自然の土壌腐植酸に近く長期間にわたりて
土壌改良効果が得られる。
Furthermore, since a portion of the product is repeatedly decomposed, reacted and mixed, the product humic acid is composed of a variety of miscellaneous components, ranging from those that have undergone advanced decomposition and reaction to those that have only slightly decomposed and reacted. Therefore, soil improvement effects can be obtained over a long period of time, similar to natural soil humic acids.

また、本発明方法を前記装置で実施する場合は、工程を
連続的に行うので処理時間が早い、うえ、製品ムラのな
い腐植酸を得ることができる。
Furthermore, when the method of the present invention is carried out using the above-mentioned apparatus, since the steps are carried out continuously, the processing time is short, and humic acid with no unevenness can be obtained.

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

第1図は本発明方法の処理工程を示すフローシート、第
2図は本発明を実施する装置の一例を示す平面図、第3
図は同側面図、第4図は第2図の要部拡大断面図である
。 1・・・原料糞タンク、5・・・混合機、7・・・添加
物タンク、11・・・加圧混練機、12・・・送り出し
装置、15・・・製品取出装置、16・・・乾燥機、1
9・・・供給装置、21・・・センサ。
FIG. 1 is a flow sheet showing the processing steps of the method of the present invention, FIG. 2 is a plan view showing an example of an apparatus for carrying out the present invention, and FIG.
The figure is a side view of the same, and FIG. 4 is an enlarged sectional view of the main part of FIG. 2. DESCRIPTION OF SYMBOLS 1... Raw material excrement tank, 5... Mixer, 7... Additive tank, 11... Pressure kneading machine, 12... Delivery device, 15... Product take-out device, 16...・Dryer, 1
9... Supply device, 21... Sensor.

Claims (5)

【特許請求の範囲】[Claims] (1)原料蓄糞にミズゴケ泥炭を主材とする添加物を混
合し、該混合物を60℃以上に加圧混練するとともに、
加圧混練した反応生成物の少なくとも一部を乾燥させた
後加圧混練前の原料糞と前記添加物の混合物に混合して
再度60℃以上に加圧混練する工程を少なくとも一回施
すことを特徴とする、蓄糞から悪臭を除去し同時に腐植
酸を製造する方法
(1) Mixing additives mainly made of sphagnum peat with the raw material accumulated dung, kneading the mixture under pressure at 60°C or higher,
After at least a part of the pressure-kneaded reaction product is dried, it is mixed with the mixture of the raw material feces before pressure-kneading and the additive, and the mixture is again pressure-kneaded at 60° C. or higher, at least once. Characteristic method of removing bad odor from accumulated feces and producing humic acid at the same time
(2)添加物が主材のミズゴケ泥炭にリグニンスルホン
酸を加えてなることを特徴とする特許請求の範囲第1項
記載の方法
(2) The method according to claim 1, characterized in that the additive is made by adding lignin sulfonic acid to the main material, sphagnum peat.
(3)添加物に予め酸処理を施すことを特徴とする特許
請求の範囲第1項及び第2項記載の方法
(3) The method according to claims 1 and 2, characterized in that the additive is subjected to acid treatment in advance.
(4)原料糞に対する添加物の混合比が10乃至30重
量%であることを特徴とする特許請求の範囲第1項乃至
第3項記載の方法
(4) The method according to claims 1 to 3, characterized in that the mixing ratio of the additive to the raw material feces is 10 to 30% by weight.
(5)加圧混練する混合物の含水率がほぼ一定になるよ
うに、原料糞と添加物の混合物の水分含有率に応じて乾
燥生成物の混合量を調整することを特徴とする特許請求
の範囲第1項乃至第4項記載の方法
(5) The amount of the dry product to be mixed is adjusted according to the moisture content of the mixture of raw material feces and additives so that the moisture content of the mixture to be kneaded under pressure is approximately constant. Methods described in Items 1 to 4 of the scope
JP59264146A 1984-12-14 1984-12-14 Method of removing bad smell and manufacturing humus acid simultaneously Granted JPS61141689A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59264146A JPS61141689A (en) 1984-12-14 1984-12-14 Method of removing bad smell and manufacturing humus acid simultaneously

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59264146A JPS61141689A (en) 1984-12-14 1984-12-14 Method of removing bad smell and manufacturing humus acid simultaneously

Publications (2)

Publication Number Publication Date
JPS61141689A true JPS61141689A (en) 1986-06-28
JPH0535117B2 JPH0535117B2 (en) 1993-05-25

Family

ID=17399096

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59264146A Granted JPS61141689A (en) 1984-12-14 1984-12-14 Method of removing bad smell and manufacturing humus acid simultaneously

Country Status (1)

Country Link
JP (1) JPS61141689A (en)

Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02120289A (en) * 1988-10-28 1990-05-08 Satoshi Inoue Method for composting livestock excreta and bedding mixture and apparatus therefor
JPH02167878A (en) * 1988-09-27 1990-06-28 Satoshi Inoue Production of organic fertilizer and apparatus therefor
WO2003071866A1 (en) * 2002-02-27 2003-09-04 Maria Perpetua King Organic absorbent material
KR20210025543A (en) * 2021-02-09 2021-03-09 (주)에코팜 Natural liquid fertilizer manufacturing method that can contain fruit coloration and sugar content and contain ginsenoside and gaba ingredients, and natural liquid fertilizer manufactured thereby
KR20220073160A (en) * 2020-11-26 2022-06-03 하철상 A method for manufacturing compost using indigenous microorganism
KR20220095480A (en) * 2020-12-30 2022-07-07 주식회사 쏠바이오 Method for manufacturing eco-friendly fermentation fertilizer composition for crop disease control and growth promotion using co-cultivation technology of bacteria and yeast
KR102430858B1 (en) * 2022-01-06 2022-08-09 주식회사 메디풀 Liquid fertilizer composition and manufacturing for therof
KR102478554B1 (en) * 2022-05-31 2022-12-16 주식회사 천지인바이오텍 Fertilizer sterilization apparatus for packaging fertilizer and sterilization method of fertilizer using the same
KR102498999B1 (en) * 2022-05-13 2023-02-13 주식회사 키움 Manufacturing method of liquid fertilizer using microbial metabolites
KR102505083B1 (en) * 2022-07-28 2023-03-03 농업회사법인 주식회사 엘바이오텍 Industrial recycling composition through fermentation decomposition of grass clippings, composition for decomposing residual pesticides, and slow-acting functional agricultural fertilizer containing the same
KR102605015B1 (en) * 2023-04-03 2023-11-23 (주)지구환경기술 Method for Preparing Liquid Fertilizer by Organic Waste Reduction Treatment using Multi-Complex Fermented Microorganisms and Environment-Friendly Liquid Fertilizer Prepared Thereby
KR102630801B1 (en) * 2022-09-08 2024-01-30 김정배 Eco-friendly crop fertilizer composition comprising fermented perilla the method for growing crops using the same

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02167878A (en) * 1988-09-27 1990-06-28 Satoshi Inoue Production of organic fertilizer and apparatus therefor
JPH02120289A (en) * 1988-10-28 1990-05-08 Satoshi Inoue Method for composting livestock excreta and bedding mixture and apparatus therefor
WO2003071866A1 (en) * 2002-02-27 2003-09-04 Maria Perpetua King Organic absorbent material
GB2400011A (en) * 2002-02-27 2004-10-06 Maria Perpetua King Organic absorbent material
KR20220073160A (en) * 2020-11-26 2022-06-03 하철상 A method for manufacturing compost using indigenous microorganism
KR20220095480A (en) * 2020-12-30 2022-07-07 주식회사 쏠바이오 Method for manufacturing eco-friendly fermentation fertilizer composition for crop disease control and growth promotion using co-cultivation technology of bacteria and yeast
KR20210025543A (en) * 2021-02-09 2021-03-09 (주)에코팜 Natural liquid fertilizer manufacturing method that can contain fruit coloration and sugar content and contain ginsenoside and gaba ingredients, and natural liquid fertilizer manufactured thereby
KR102430858B1 (en) * 2022-01-06 2022-08-09 주식회사 메디풀 Liquid fertilizer composition and manufacturing for therof
KR102498999B1 (en) * 2022-05-13 2023-02-13 주식회사 키움 Manufacturing method of liquid fertilizer using microbial metabolites
KR102478554B1 (en) * 2022-05-31 2022-12-16 주식회사 천지인바이오텍 Fertilizer sterilization apparatus for packaging fertilizer and sterilization method of fertilizer using the same
KR102505083B1 (en) * 2022-07-28 2023-03-03 농업회사법인 주식회사 엘바이오텍 Industrial recycling composition through fermentation decomposition of grass clippings, composition for decomposing residual pesticides, and slow-acting functional agricultural fertilizer containing the same
KR102630801B1 (en) * 2022-09-08 2024-01-30 김정배 Eco-friendly crop fertilizer composition comprising fermented perilla the method for growing crops using the same
KR102605015B1 (en) * 2023-04-03 2023-11-23 (주)지구환경기술 Method for Preparing Liquid Fertilizer by Organic Waste Reduction Treatment using Multi-Complex Fermented Microorganisms and Environment-Friendly Liquid Fertilizer Prepared Thereby

Also Published As

Publication number Publication date
JPH0535117B2 (en) 1993-05-25

Similar Documents

Publication Publication Date Title
US5393317A (en) Method and apparatus for producing organic based fertilizer in continuous process
JPS61141689A (en) Method of removing bad smell and manufacturing humus acid simultaneously
CN105948866A (en) Method for preparing humus organic fertilizer from pond silt and sewage treatment plant sludge
Haga Development of composting technology in animal waste treatment-review
CN104876734A (en) Organic fertilizer and preparation method thereof
CN110357727A (en) A kind of charcoal base organic fertilizer and its production method
US20200354284A1 (en) Preparing organic fertilizer from agricultural wastes and livestock manure
CZ303821B6 (en) Organic fertilizer and process for preparing thereof
EP0480030B1 (en) Method and apparatus for composting mixture of livestock excretion and barn mat
RU2214990C1 (en) Method for processing organic waste products
CN106631351A (en) Preparation method of farmyard manure for corn planting
KR100881849B1 (en) Apparatus of organic fertilizer
CN108299032A (en) A method of quickly preparing organic fertilizer
CN104892172A (en) Production technique of shell-powder-added organic fertilizer
CN110357682A (en) The preparation method of charcoal base soil conditioner for Radix Glehniae plantation
CZ32099A3 (en) Process and apparatus for producing compost
CN114539005A (en) Method for preparing organic fertilizer by using crop straws
CN107500979A (en) A kind of preparation method of the special farm manure of wheat
Bianchi et al. Characterization of composting mixtures and compost of rabbit by-products to obtain a quality product and plant proposal for industrial production.
Rautela et al. Vermicompost is boon to enrichment of micronutrient content in soil
WO2006109968A1 (en) Perfectly fermented compost and method for manufacturing thereof
DE102007056840A1 (en) Method and device for producing a ready-prepared fermentation substrate for biogas production
RU2749075C1 (en) Method for preparing feed additive from organic waste
Castillo et al. Influence of earthworms on organic waste composting and charactertisation of vermicompost end products
CN108101592A (en) A kind of organic fertilizer fermentation method

Legal Events

Date Code Title Description
R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

EXPY Cancellation because of completion of term