JP2003055081A - Sludge fermented fertilizer - Google Patents

Sludge fermented fertilizer

Info

Publication number
JP2003055081A
JP2003055081A JP2001243760A JP2001243760A JP2003055081A JP 2003055081 A JP2003055081 A JP 2003055081A JP 2001243760 A JP2001243760 A JP 2001243760A JP 2001243760 A JP2001243760 A JP 2001243760A JP 2003055081 A JP2003055081 A JP 2003055081A
Authority
JP
Japan
Prior art keywords
sludge
fertilizer
fermenting
raw material
soil
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
JP2001243760A
Other languages
Japanese (ja)
Other versions
JP4875809B2 (en
Inventor
Taiji Murohara
泰二 室原
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
FUTABA GREEN DOBOKU KK
Original Assignee
FUTABA GREEN DOBOKU 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 FUTABA GREEN DOBOKU KK filed Critical FUTABA GREEN DOBOKU KK
Priority to JP2001243760A priority Critical patent/JP4875809B2/en
Publication of JP2003055081A publication Critical patent/JP2003055081A/en
Application granted granted Critical
Publication of JP4875809B2 publication Critical patent/JP4875809B2/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

Abstract

PROBLEM TO BE SOLVED: To provide a novel sludge fermented fertilizer which has an excellent plant growth effect, can be inexpensively manufactured by utilizing wastes and is sufficiently progressed in fermentation so as to perish unnecessary saprophytic bacteria, seeds, etc. SOLUTION: This sludge fermented fertilizer is formed by compounding putrefactive organic materials and seashell incineration ash to a raw material mixture composed of bark compost, sludge, livestock night soil and soil conditioners at need and further adding microorganisms thereto and subjecting the mixture to fermentation and maturation. Coconut husks, cedar bark, peat- moss, vermiculite, coconut husk charcoal, charcoal, charcoal dust, etc., are adequately used as the soil conditioners.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、肥料の技術分野に
属する。
TECHNICAL FIELD The present invention belongs to the technical field of fertilizers.

【0002】[0002]

【従来の技術】除草剤、殺菌剤等の農薬の使用や、化学
肥料の連用によって地力が低下することは良く知られた
ことである。このような地力の低下の主要因は、土壌有
機物および土壌有効微生物の減少によるものであり、そ
の対策として、堆肥等の有機質肥料の施用、有効微生物
活性剤の施用などが行われている。しかし、従来提案さ
れている有機質肥料等は、その植物育成効果が十分でな
かったり、コスト・パフォーマンスが十分でなかったり
して、まだ十分満足できるものではない。
2. Description of the Related Art It is well known that the use of pesticides such as herbicides and fungicides, and the continuous use of chemical fertilizers lowers the soil fertility. The main cause of such decrease in soil fertility is due to the decrease of soil organic matter and soil effective microorganisms. As countermeasures for this, application of organic fertilizer such as compost and application of effective microbial activator have been carried out. However, the organic fertilizers and the like that have been proposed so far are not yet fully satisfactory, because their plant-growing effects are not sufficient and their cost performance is not sufficient.

【0003】一方、近年、一般廃棄物あるいは産業廃棄
物は、その量、種類ともにますます増大し、その処理が
重大な問題となっている。かかる廃棄物の有効利用の一
環として、土地開発のため伐採した木材、抜根した根、
森林育成のため間伐した間伐木材、剪定枝、あるいは木
造家屋等の解体木材等の木質廃棄物をチップ加工し、そ
れを微生物を利用して発酵、熟成させてバーク堆肥とな
し、あるいは、いわゆる生ゴミを微生物を利用して発
酵、熟成させて堆肥となし、それらを有機質肥料等とし
て有効利用することは良く知られている。しかし、その
利用量は少なく、廃棄物を十分に有効利用する方法は未
だ見出されてないのが現状であった。
On the other hand, in recent years, the amount and kind of general waste or industrial waste have been increasing, and the treatment thereof has become a serious problem. As part of the effective use of such waste, timber harvested for land development, rooted roots,
Wood waste such as thinned wood thinned to grow forests, pruned branches, or demolition wood such as wooden houses is processed into chips and fermented and aged using microorganisms to form bark compost, or so-called raw It is well known that fermenting and aging wastes to form compost by utilizing microorganisms and effectively utilizing them as organic fertilizers and the like. However, the amount of the waste used is small, and a method for effectively utilizing the waste has not yet been found.

【0004】このような状況の中、本発明者は、優れた
植物育成効果を有し、かつ廃棄物が有効利用され安価に
製造できる肥料(土壌基盤材)を発明し、既に特許出願
を行っている(特開2001−48687号)。この発
明は、バーク堆肥、汚泥、黒土、畜産下肥および貝殻焼
却灰を必須成分とする原材料混合物に微生物を加え、該
原材料混合物を発酵、熟成させて得られる土壌基盤材で
ある。これにより、例えば、排水処理施設等から排出さ
れる汚泥や、建設残土の黒土などの有効利用を図ること
ができる。しかしながら、上記土壌基盤材は、黒土を相
当量含むことから、全体に占める微生物の相対量が小さ
くなり、すなわち微生物の密度が低下してしまい、その
ために高い発酵温度を得ることができなかった。したが
って、例えば、下水処理場の汚泥にトマトの種が含まれ
ている場合に、発酵によってその種が完全には死滅せ
ず、肥料化した段階で発芽してしまうという問題が生
じ、さらなる改良が望まれていた。
Under these circumstances, the present inventor has invented a fertilizer (soil base material) which has an excellent plant-growing effect and can effectively produce waste and can be manufactured at low cost, and has already filed a patent application. (Japanese Patent Laid-Open No. 2001-48687). This invention is a soil base material obtained by adding microorganisms to a raw material mixture containing bark compost, sludge, black soil, livestock manure and shell incineration ash as essential components, and fermenting and aging the raw material mixture. As a result, for example, it is possible to effectively utilize sludge discharged from a wastewater treatment facility or the like, or black soil left over from construction. However, since the soil base material contains a considerable amount of black soil, the relative amount of the microorganisms in the whole becomes small, that is, the density of the microorganisms is lowered, and therefore a high fermentation temperature cannot be obtained. Therefore, for example, when tomato seeds are contained in the sludge of a sewage treatment plant, there is a problem that the seeds are not completely killed by fermentation and germination occurs at the stage of fertilization, and further improvement is required. Was wanted.

【0005】[0005]

【発明が解決しようとする課題】そこで本発明は、上記
従来の状況に鑑み、優れた植物育成効果を有し、かつ廃
棄物を有効利用して安価に製造できる肥料であって、不
要な雑菌や種などが死滅するように発酵を十分に進行さ
せた、新規な汚泥発酵肥料を提供することを目的とす
る。
In view of the above-mentioned conventional circumstances, the present invention is a fertilizer which has an excellent plant-growing effect and can be produced inexpensively by effectively utilizing waste, and which is an unnecessary germ. It is an object of the present invention to provide a novel sludge fermenting fertilizer in which fermentation is sufficiently advanced so that seeds, seeds and the like are killed.

【0006】[0006]

【課題を解決するための手段】上記課題を解決するた
め、本発明の汚泥発酵肥料は、バーク堆肥、汚泥、畜産
下肥、及び土壌改良材を必須成分とする原材料混合物に
対し、必要に応じて、腐敗性の有機物質や貝殻焼却灰を
配合し、さらに微生物を加え、発酵、熟成させたことを
特徴とする。
In order to solve the above-mentioned problems, the sludge fermenting fertilizer of the present invention is used for bark compost, sludge, livestock manure, and a raw material mixture containing soil improver as an essential component, if necessary. Then, a perishable organic substance and incinerated shell ash are blended, and microorganisms are further added, followed by fermentation and aging.

【0007】上記構成によれば、従来廃棄物とされてき
たバーク堆肥や、施設等から排出される各種汚泥、及び
貝殻焼却灰などの有効利用が図られるとともに、70〜
80℃程度の高い発酵温度が得られ、雑菌等が死滅す
る。
According to the above construction, the bark compost, which has been conventionally regarded as waste, various sludges discharged from facilities, etc., and the incineration ash of shells can be effectively used, and 70-
A high fermentation temperature of about 80 ° C is obtained, and various bacteria and the like die.

【0008】[0008]

【発明の実施の形態】以下、本発明を詳細に説明する。
本発明の汚泥発酵肥料は、バーク堆肥、汚泥、畜産下
肥、及び土壌改良材を必須成分とする原材料混合物に対
し、微生物を加え、発酵、熟成させて概略構成される。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention will be described in detail below.
The sludge fermenting fertilizer of the present invention is roughly constructed by adding microorganisms to a raw material mixture containing bark compost, sludge, livestock manure, and soil conditioner as essential components, fermenting and aging.

【0009】バーク堆肥としては、従来知られたバーク
堆肥を適宜選択して用いることができる。バーク堆肥
は、一般に、土地開発のため伐採した木材、抜根した
根、森林育成のため間伐した間伐木材、剪定枝、あるい
は木造家屋等の解体木材等の木質廃棄物をチップ加工
し、その一部を微生物を利用して発酵、熟成させて製造
される。バーク堆肥を用いることは、木質廃棄物の有効
利用をなしたこととなる。このバーク堆肥は、市販品を
適宜選択して用いても良いし、本発明の原材料用に木質
廃棄物から常法により製造しても良い。なお、チップ化
した一部を木炭、粉炭に加工したものは、後述の土壌改
良材として本発明の原材料に利用することができる。
As the bark compost, conventionally known bark compost can be appropriately selected and used. Generally, bark compost is made by chipping wood waste such as timber cut for land development, rooted root, thinned wood thinned for forest development, pruned branches, or demolition wood such as wooden houses, and part of it. Is produced by fermenting and aging the microorganisms using microorganisms. The use of bark compost is an effective use of wood waste. As the bark compost, a commercially available product may be appropriately selected and used, or the bark compost may be produced from a wood waste for a raw material of the present invention by a conventional method. It should be noted that the chipped part, which is processed into charcoal or pulverized coal, can be used as a soil improving material described later as a raw material of the present invention.

【0010】上記バーク堆肥の製造に際しては、微生物
として、従来知られたものを適宜選択して用いることが
でき、一般に、放線菌、光合成菌、乳酸菌、糸状菌、酵
母等から選ばれた少なくとも一種が用いられるが、中で
も、抗酸性で乳酸を生産し酪酸を生産せず病原性を有さ
ずかつ拮抗価50以上である有効微生物群(Effec
tive Micro−orgamisms:以下
「EM菌」と略称する)が好ましく用いられる。このE
M菌は、自然界に存在する微生物の内の農業生産などに
有用な放線菌、光合成菌、乳酸菌、糸状菌、酵母などの
5科10属80余種の嫌気性と好気性の微生物を含むも
のである。このEM菌中の放線菌の例として、Stre
pto−myces sp.(ATCC 3004)、
Streptoverticillium sp.(A
TCC 23654)、Nocardia sp.(A
TCC 19247)、Micromonospora
sp.(ATCC 12452)、Rhodococ
cussp.等が挙げられ、光合成菌の例として、Rh
odopseudomonas sp.(R.spha
eroldes)、Rhodosplrillum s
p.(R.fulum)、Chromatium s
p.(C.okenii)、Chlorobium s
p.(C.limicola)等が挙げられ、乳酸菌
(乳酸生成菌)の例として、Lactobacillu
s sp. (IFO 3070)、Propioni
bacterium sp.(P.freudenre
ichii)、Pediococcus sp.(P.
halophilus)、Streptococcus
sp.(S.lactis、S.faecalis)
等が挙げられ、糸状菌の例として、Aspergill
us sp.(RIFY 5770、RIFY 502
4)、Mucor sp.(IFO 8567)等が挙
げられ、酵母の例として、Saccharomyces
sp.(NRRL 1346、Y977)、Cand
ida sp.(C.utilis)等が挙げられる。
また、このEM菌には、各種市販品があり、各種市販品
を適宜選択して用いることもできる。
In the production of the bark compost, conventionally known microorganisms can be appropriately selected and used as the microorganisms, and generally, at least one selected from actinomycetes, photosynthetic bacteria, lactic acid bacteria, filamentous fungi, yeasts and the like. Among them, the effective microorganism group (Effec) which is anti-acidic and produces lactic acid, does not produce butyric acid, has no pathogenicity, and has an antagonistic value of 50 or more.
live Micro-organisms: Below
"Abbreviated as" EM bacterium ") is preferably used. This E
M bacteria include actinomycetes, photosynthetic bacteria, lactic acid bacteria, filamentous fungi, yeasts and other anaerobic and aerobic microorganisms of 5 families, 10 genera and 80 species which are useful for agricultural production among microorganisms existing in nature. . As an example of actinomycetes in this EM strain,
pto-myces sp. (ATCC 3004),
Streptoverticillium sp. (A
TCC 23654), Nocardia sp. (A
TCC 19247), Micromonospora.
sp. (ATCC 12452), Rhodococ
cussp. As an example of the photosynthetic bacterium, Rh
odopseudomonas sp. (R.spha
eroldes), Rhodosprilillum s
p. (R. fulum), Chromatium s
p. (C. okenii), Chlorobium s
p. (C. limicola) and the like, and examples of lactic acid bacteria (lactic acid-producing bacteria) include Lactobacillus.
s sp. (IFO 3070), Propioni
Bacterium sp. (P. freudenre
ichii), Pediococcus sp. (P.
halophilus), Streptococcus
sp. (S. lactis, S. faecalis)
As an example of the filamentous fungus, Aspergill
us sp. (RIFY 5770, RIFY 502
4), Mucor sp. (IFO 8567) and the like, and examples of yeast include Saccharomyces.
sp. (NRRL 1346, Y977), Cand
ida sp. (C. utilis) and the like.
Further, there are various commercially available products of this EM bacterium, and various commercially available products can be appropriately selected and used.

【0011】次に、汚泥としては、例えば上下水道に関
わる浄水処理施設、下水処理施設、あるいは工場その他
の排水に関わる排水処理施設等の諸施設から排出される
各種汚泥を適宜用いることができる。一般に、汚泥は、
水分が多く、腐敗して異臭を発散し、その有効利用がな
かなか難しい廃棄物であるが、本発明によれば、かかる
汚泥を、肥料として好適に有効利用することができる。
本発明の原材料として用いるに当たり、汚泥の水分含有
量は、特に制限する必要なく適宜設定することができ、
必要に応じて脱水ないし乾燥して適宜調整することがで
きるが、一般には、75〜90重量%が適当である。
Next, as the sludge, for example, various sludges discharged from various facilities such as water purification and sewage treatment facilities, sewage treatment facilities, and factories and other wastewater treatment facilities related to wastewater can be appropriately used. Generally, sludge is
Although it is a waste that has a large amount of water, decomposes and emits an offensive odor, and its effective utilization is difficult, according to the present invention, such sludge can be effectively utilized as a fertilizer.
When used as a raw material of the present invention, the water content of the sludge can be appropriately set without any particular limitation,
It can be appropriately adjusted by dehydration or drying if necessary, but in general, 75 to 90% by weight is suitable.

【0012】また、畜産下肥としては、従来から知られ
た牛肥、豚肥、鶏糞等の畜産下肥を適宜選択して用いる
ことができ、必要に応じて複数種の畜産下肥を併用する
こともできる。これら畜産下肥は、市販品を適宜選択し
て用いても良いし、本発明の原材料用に畜産動物の排泄
物から常法により製造しても良い。また、これら畜産下
肥は、一般に、その使用量を増減させて、本発明の肥料
を所定の有機成分含有量とするための有機成分調節材と
して機能させることができる。また、その使用量を増減
させて、発酵、熟成処理に付す原材料混合物を所定の水
分含有量とするための水分含有量調節材として機能させ
ることもできる。
As the livestock manure, conventionally known livestock manure such as beef manure, pig manure, and chicken manure can be appropriately selected and used. If necessary, a plurality of kinds of livestock manure can be used in combination. You can also do it. These livestock manure may be appropriately selected from commercially available products, or may be produced from the excrement of livestock animals by the conventional method for the raw material of the present invention. In addition, these livestock manure can generally function as an organic component adjusting material for increasing or decreasing the amount of use thereof so that the fertilizer of the present invention has a predetermined organic component content. It is also possible to increase / decrease the amount used and to function as a water content adjusting material for making the raw material mixture subjected to fermentation and aging treatment a predetermined water content.

【0013】さらに、土壌改良材としては、従来知られ
た土壌改良材を適宜選択して用いることができるが、具
体的には、ヤシ殻、杉バーク、ピートモス、バーミキュ
ライト、ヤシ殻炭、木炭、粉炭等が好ましく用いられ
る。これらの土壌改良材は、一種配合することもできる
し、二種以上配合することもできる。特に、杉バーク又
はピートモスと、ヤシ殻(ヤシ殻炭を含む)との組み合
わせは、発酵が効率よく進み、良質の肥料を得やすいた
め最も好ましく採用される。
Further, as the soil improving material, conventionally known soil improving materials can be appropriately selected and used. Specifically, coconut shell, cedar bark, peat moss, vermiculite, coconut shell charcoal, charcoal, Pulverized coal or the like is preferably used. These soil conditioners can be used alone or in combination of two or more. In particular, the combination of cedar bark or peat moss and coconut shell (including coconut shell charcoal) is most preferably adopted because the fermentation proceeds efficiently and a high-quality fertilizer is easily obtained.

【0014】本発明の汚泥発酵肥料は、上記のようなバ
ーク堆肥、汚泥、畜産下肥、及び土壌改良材を必須成分
として用い、これら各原材料を混合した原材料混合物に
微生物を加え、それを発酵、熟成させることにより製造
される。その際、各原材料の配合割合は、各原材料の性
状、特性等によって一概にはいえないが、一般に、バー
ク堆肥を25〜35重量部、汚泥を20〜30重量部、
畜産下肥を25〜35重量部、土壌改良材を8〜15重
量部程度とすることが適当である。特に、土壌改良材と
して、上述したような、杉バーク又はピートモスとヤシ
殻とを併用する場合は、杉バーク又はピートモスを4〜
6重量部、ヤシ殻を4〜9重量部とすることが好まし
い。
The sludge fermenting fertilizer of the present invention uses the above-described bark compost, sludge, livestock manure, and soil improving material as essential components, and adds microorganisms to a raw material mixture obtained by mixing these raw materials and fermenting it. Manufactured by aging. At that time, the mixing ratio of each raw material cannot be generally determined depending on the properties, characteristics, etc. of each raw material, but generally 25 to 35 parts by weight of bark compost, 20 to 30 parts by weight of sludge,
It is suitable that the livestock manure is about 25 to 35 parts by weight and the soil conditioner is about 8 to 15 parts by weight. In particular, when the cedar bark or peat moss and coconut shell are used in combination as the soil improving material, the cedar bark or peat moss is 4 to
It is preferable that 6 parts by weight and 4 to 9 parts by weight of coconut shell are used.

【0015】また、原材料混合物には、必要に応じて、
上記必須成分に加え、さらに腐敗性の有機物質を配合す
ることができる。この腐敗性有機物質の例として、米
糠、油粕、魚粉、糖蜜、生ゴミ等が挙げられる。これら
の腐敗性有機物質は一種配合することもできるし、二種
以上配合することもできる。また、腐敗性有機物質の配
合量は、それらの種類、性状等によって一概にはいえな
いが、一般に、必須成分の各原材料の合計を100重量
部としたとき、1〜13重量部が適当である。
The raw material mixture may contain, if necessary,
In addition to the above essential components, a perishable organic substance can be further added. Examples of this putrefactive organic substance include rice bran, oil cake, fish meal, molasses, and garbage. These septic organic substances may be blended in one kind or in two or more kinds. Further, the amount of the putrefactive organic substance to be blended cannot be generally determined depending on their types, properties, etc., but in general, 1 to 13 parts by weight is appropriate when the total amount of each of the essential ingredients is 100 parts by weight. is there.

【0016】さらに、原材料混合物には、必要に応じ
て、上記必須成分に加え、貝殻焼却灰を配合することが
できる。貝殻焼却灰としては、貝殻を焼却し粉砕してあ
るいは粉砕し焼却して得られた貝殻焼却灰が用いられ
る。原料の貝殻はその由来は問うことなく任意である
が、この原料貝殻として、例えば発電所、工場等におけ
る海水と接触する諸設備、例えば冷却用海水の配管等に
付着していた貝であって、その諸設備の機能保全メンテ
ナンスにおいて廃棄物として取り出された貝を用いれ
ば、この貝殻焼却灰の使用も廃棄物の有効利用に他なら
ない。この貝殻焼却灰は、発酵、熟成処理に付す原材料
混合物の酸性度を調整する機能を有する。すなわち、上
記汚泥は酸性であることが多いので、貝殻焼却灰がその
中和剤として機能する。本発明において、発酵、熟成処
理に付す原材料混合物のpHは、一般に6.5〜7.3
が適当である。また、貝殻焼却灰は、汚泥発酵肥料を土
壌に施用したときに、その土壌を中和し、かつカルシウ
ム源としても機能するものである。なお、上記貝殻焼却
灰は、予め原材料混合物に配合する代わりに、本発明の
汚泥発酵肥料を土壌に施用する際に一緒に施用しても良
い。
Further, the raw material mixture may be mixed with shell incineration ash, if necessary, in addition to the above-mentioned essential components. As the shell incineration ash, shell shell incineration ash obtained by incinerating and crushing shells or crushing and incinerating is used. The shell of the raw material is arbitrary regardless of its origin, but as the shell of this raw material, for example, various facilities that come into contact with seawater at power plants, factories, etc. If shellfish taken out as waste in the functional maintenance of the various facilities are used, the use of this shell incineration ash is nothing but effective use of waste. This shell incineration ash has a function of adjusting the acidity of the raw material mixture subjected to fermentation and aging treatments. That is, since the above-mentioned sludge is often acidic, shell incineration ash functions as its neutralizing agent. In the present invention, the pH of the raw material mixture subjected to fermentation and aging treatment is generally 6.5 to 7.3.
Is appropriate. In addition, the shell incineration ash neutralizes the soil when the sludge fertilizer is applied to the soil, and also functions as a calcium source. The shell ash may be applied together with the sludge fermenting fertilizer of the present invention when applied to soil, instead of being preliminarily mixed with the raw material mixture.

【0017】次に、原材料混合物に加える微生物として
は、上述の、木質廃棄物からのバーク堆肥の製造の際と
同様の微生物を用いることができる。すなわち、従来知
られた微生物を適宜選択して用いることができ、一般
に、放線菌、光合成菌、乳酸菌、糸状菌、酵母等から選
ばれた少なくとも一種が用いられ、中でも、EM菌が好
ましく用いられる。微生物の添加量は、添加される微生
物の形態、原材料混合物の組成等によって異なり一概に
はいえないが、微生物が、いわゆるボカシ(有機物質を
EM菌などの微生物で予め発酵させたもの)の形態であ
るとすれば、一般に、原材料混合物を100重量部とし
たとき、1.0〜3.0重量部が適当である。
Next, as the microorganisms to be added to the raw material mixture, the same microorganisms as in the above-described production of bark compost from wood waste can be used. That is, conventionally known microorganisms can be appropriately selected and used, and generally, at least one selected from actinomycetes, photosynthetic bacteria, lactic acid bacteria, filamentous fungi, yeasts and the like is used, and among them, EM bacteria are preferably used. . The amount of microorganisms added varies depending on the form of the added microorganisms, the composition of the raw material mixture, etc., and cannot be generally stated, but the form of so-called blurring (organic substances pre-fermented with microorganisms such as EM bacteria) In general, 1.0 to 3.0 parts by weight is suitable when the raw material mixture is 100 parts by weight.

【0018】なお、上述のように、微生物をボカシの形
態で加える場合、そのボカシは、例えば米糠、油粕、魚
粉、糖蜜などの有機物質と微生物とを混合し発酵させた
ものであるが、特に、糖蜜を、ボカシ全体に対して0.
15〜0.25重量%程度含むことが好ましい。これに
より、微生物が速やかに繁殖し、活動が活発になる。そ
のため、例えば、仮に原材料の一つであるバーク堆肥の
熟成が不十分(いわゆる半生状態)であったとしても本
発明に使用することができ、原材料の選択の幅、利用範
囲が広がる。また、高い発酵温度を得やすくなるという
顕著な効果を奏する。
As described above, when the microorganisms are added in the form of blur, the blur is obtained by mixing and fermenting the microorganisms with an organic substance such as rice bran, oil cake, fish meal and molasses. , Molasses, 0.
It is preferable to contain about 15 to 0.25% by weight. As a result, the microorganisms rapidly reproduce and become active. Therefore, for example, even if bark compost, which is one of the raw materials, is not sufficiently matured (so-called semi-raw state), it can be used in the present invention, and the range of selection of raw materials and the range of utilization are widened. Further, it has a remarkable effect that it is easy to obtain a high fermentation temperature.

【0019】原材料混合物に微生物を加えて発酵、熟成
させるには、従来知られた堆肥等の有機質肥料を製造す
る際の方法に準じて行うことができる。例えば、原材料
混合物に微生物の固形培養物を添加混合し、それを密封
容器に入れて所定温度に、所定時間保持して行うことが
でき、また微生物の固形培養物に代えて微生物の培養液
を用いることもできる。また、発酵、熟成の処理条件
は、原材料混合物の組成、用いた微生物の種類等必要に
応じて適宜設定することができるが、一般に、原材料混
合物の水分含有量は10〜40重量%が好ましく、その
pHは6.5〜7.3程度であることが好ましい。ま
た、本発明においては、発酵温度が80℃程度にまで上
昇するため、雑菌、不要な種などが死滅し、より上質な
肥料が得られる。なお、発酵、熟成期間は、処理温度に
もよるが、一般に2〜8ヶ月で完熟して、目的の汚泥発
酵肥料が得られる。
In order to add a microorganism to the mixture of raw materials and to ferment and ripen it, it can be carried out according to a method known in the art for producing an organic fertilizer such as compost. For example, a solid culture of a microorganism may be added to and mixed with the raw material mixture, and the mixture may be placed in a sealed container at a predetermined temperature for a predetermined period of time, and the culture liquid of the microorganism may be replaced with the solid culture of the microorganism. It can also be used. Further, the processing conditions of fermentation and aging can be appropriately set as necessary such as the composition of the raw material mixture and the type of microorganism used, but generally, the water content of the raw material mixture is preferably 10 to 40% by weight, The pH is preferably about 6.5 to 7.3. Further, in the present invention, since the fermentation temperature rises to about 80 ° C., various bacteria and unnecessary species are killed, and a higher quality fertilizer can be obtained. It should be noted that the fermentation and maturation periods, which depend on the treatment temperature, are generally completed in 2 to 8 months to obtain the desired sludge fertilizer.

【0020】本発明の汚泥発酵肥料は、優れた植物育成
効果を有し、かつ安価に製造できる等の優れた特性を有
していて、種々の用途に幅広く用いることができる。そ
の例として、樹木の植栽用土ないしその有機質肥料、家
庭園芸用土ないしその有機質肥料、鉢植用土、稲作ある
いは畑作の有機質肥料等が挙げられる。
The sludge-fermenting fertilizer of the present invention has excellent plant-growing effects and excellent properties such that it can be produced at low cost, and can be widely used for various purposes. Examples thereof include soil for planting trees or organic fertilizers therefor, soil for home gardening or organic fertilizers therefor, potting soil, organic fertilizers for rice cultivation or upland cultivation, and the like.

【0021】[0021]

【実施例】以下、実施例により本発明をさらに詳細に説
明するが、これらに限定されるものではない。 (実施例1)バーク堆肥(間伐材木から微生物として市
販のEM菌を用いて製造したもの)30重量部、下水処
理施設から排出された汚泥(脱水ケーキ)25重量部、
牛肥30重量部、ヤシ殻8重量部、及び杉バーク5重量
部から原材料混合物を構成した。原材料混合物は、水分
含有量が75重量%で、pHは6.8であった。この原
材料混合物に、ボカシ2重量部を加えて撹拌混合した。
なお、ボカシとしては、米糠20kg、油粕7.0k
g、魚粉7.0kg、糖蜜0.05kgにEM菌を加え
て発酵させたものを用いた。続いて、攪拌混合したもの
をビニール袋に充填して密閉し、2.5ヶ月間保持して
発酵、熟成を行い、目的の汚泥発酵肥料を製造した。
EXAMPLES The present invention will be described in more detail with reference to examples below, but the invention is not limited thereto. (Example 1) 30 parts by weight of bark compost (produced from thinned wood using commercially available EM bacteria as a microorganism), 25 parts by weight of sludge (dehydrated cake) discharged from a sewage treatment facility,
A raw material mixture was composed of 30 parts by weight of beef manure, 8 parts by weight of coconut shell, and 5 parts by weight of cedar bark. The raw material mixture had a water content of 75% by weight and a pH of 6.8. To this raw material mixture, 2 parts by weight of blur was added and mixed with stirring.
In addition, as for blurring, rice bran 20 kg, oil cake 7.0 k
g, fish meal 7.0 kg, molasses 0.05 kg, and fermented by adding EM bacteria. Then, the mixture mixed with stirring was filled in a vinyl bag, sealed, and held for 2.5 months for fermentation and aging to produce a target sludge fertilizer.

【0022】次に、得られた汚泥発酵肥料の施用によ
る、こまつな(ツケナ類)の発芽、及び発芽後の生育へ
の支障の有無・程度を調べるため、幼植物試験を実施し
た。また、対照肥料として、市販のバーク堆肥を用い、
同様の試験を行った。(表1)に供試肥料(汚泥発酵肥
料)及び対照肥料の分析成績、(表2)に供試土壌の土
性及び沖積土又は洪積土の別、(表3)に試験区及び施
肥の設計内容、(表4)に栽培方法及び管理の状況、そ
して試験結果として、(表5)に発芽及び生育調査成績
並びに異常症状の有無を示す。
Next, a seedling test was carried out to examine the presence or extent of the germination of Komatsuna (Apis crusica) and the hindrance to the growth after germination by applying the obtained sludge fertilizer. In addition, as a reference fertilizer, using a commercially available bark compost,
A similar test was conducted. (Table 1) shows the analysis results of the test fertilizer (sludge fermentation fertilizer) and control fertilizer, (Table 2) shows the soil properties of the test soil and alluvial soil or diluvial soil, and (Table 3) the test area and fertilizer application. The design contents, (Table 4) shows the cultivation method and management status, and as test results, (Table 5) shows the results of germination and growth investigations and the presence or absence of abnormal symptoms.

【0023】[0023]

【表1】 [Table 1]

【表2】 [Table 2]

【表3】 [Table 3]

【表4】 [Table 4]

【表5】 [Table 5]

【0024】なお、供試肥料に含まれるNは、乾物換算
値で2%以下であるため、通達の試験方法に基づき、供
試及び対照の両肥料の試験区の施肥量は、それぞれの肥
料の乾物重量を基準として設定した。また、上記(表
3)に記載した供試及び対照肥料のすべての試験区並び
に供試及び対照の両肥料の無施肥として設けた無機基礎
量区に、N、P25、及びK2Oとしてそれぞれ25m
gに相当する量の硫酸アンモニア、過リン酸石灰、及び
塩化カリを施肥した。なお、上記(表3)の施用量欄中
の括弧内数値は、有姿(現物)の量を示す。
Since the N contained in the test fertilizer is 2% or less in terms of dry matter, the fertilizer application rates of both the test and control fertilizers in the test plots are based on the conventional test method. It was set based on the dry matter weight. In addition, N, P 2 O 5 , and K 2 were added to all the test plots of the test and control fertilizers described in (Table 3) above and the inorganic basic amount plots provided without fertilization of both the test and control fertilizers. 25m each as O
An amount of ammonium sulfate, lime superphosphate, and potassium chloride was applied in an amount corresponding to g. The values in parentheses in the application column of the above (Table 3) indicate the amount in the physical form (actual).

【0025】上記の試験の結果、(表5)に示すよう
に、供試肥料区は、無機基礎量区に比べて、発芽につい
ては、発芽開始日及び発芽率とも同等程度の成績を示
し、また発芽後の生育においては、同等以上の成績を示
して、有害物によると考えられる植物の生育上の異常症
状は認められなかった。
As a result of the above-mentioned test, as shown in (Table 5), the fertilizer plots showed similar results in germination start date and germination rate with respect to germination as compared with the inorganic basic amount plots. In the post-emergence growth, the same or better performance was shown, and no abnormal growth symptoms of the plant considered to be due to harmful substances were observed.

【0026】[0026]

【発明の効果】以上、本発明の汚泥発酵肥料は、優れた
植物育成効果を有し、かつ廃棄物の有効利用に資するも
のであり、また製造コストも安価に抑えることができ
る。さらに高い発酵温度が得られるので、雑菌等が死滅
して良質の肥料が得られる。本発明の汚泥発酵肥料は、
上記の優れた特性から、幅広い用途において有用であ
る。
INDUSTRIAL APPLICABILITY As described above, the sludge fermenting fertilizer of the present invention has an excellent plant growing effect, contributes to effective use of waste, and can be manufactured at low cost. Since a higher fermentation temperature can be obtained, various bacteria and the like can be killed and a high-quality fertilizer can be obtained. The sludge fermentation fertilizer of the present invention,
Due to the above excellent properties, it is useful in a wide range of applications.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C05F 11:00 C05F 3:00 3:00 5:00 5:00 1:00 1:00 9:00 9:00) Fターム(参考) 4D059 AA01 AA03 AA07 BA01 BA22 BA25 DA60 DA64 DA70 DB32 DB33 4H061 AA01 CC32 CC36 CC42 CC46 CC47 CC51 CC55 DD14 EE46 EE51 EE64 EE66 FF06 GG48 HH07 LL25 LL26 ─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification code FI theme code (reference) C05F 11:00 C05F 3:00 3:00 5:00 5:00 5:00 1:00 1:00 9:00 9 : 00) F term (reference) 4D059 AA01 AA03 AA07 BA01 BA22 BA25 DA60 DA64 DA70 DB32 DB33 4H061 AA01 CC32 CC36 CC42 CC46 CC47 CC51 CC55 DD14 EE46 EE51 EE64 EE66 FF06 GG48 HH07 LL25 LL26

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】 バーク堆肥、汚泥、畜産下肥、及び土壌
改良材を必須成分とする原材料混合物に対し、微生物を
加え、発酵、熟成させてなる汚泥発酵肥料。
1. A sludge-fermenting fertilizer obtained by fermenting and aging microorganisms to a mixture of raw materials containing bark compost, sludge, livestock manure, and soil conditioner as essential components.
【請求項2】 請求項1記載の汚泥発酵肥料において、
土壌改良材が、ヤシ殻、杉バーク、ピートモス、バーミ
キュライト、ヤシ殻炭、木炭、粉炭から選ばれる一種以
上であることを特徴とする汚泥発酵肥料。
2. The sludge fermentation fertilizer according to claim 1,
A sludge fermenting fertilizer characterized in that the soil improving material is one or more kinds selected from coconut shell, cedar bark, peat moss, vermiculite, coconut shell charcoal, charcoal and pulverized coal.
【請求項3】 請求項1又は2記載の汚泥発酵肥料にお
いて、必須成分の配合割合が、バーク堆肥25〜35重
量部、汚泥20〜30重量部、畜産下肥25〜35重量
部、土壌改良材8〜15重量部であることを特徴とする
汚泥発酵肥料。
3. The sludge fermenting fertilizer according to claim 1, wherein the mixing ratio of the essential components is 25 to 35 parts by weight of bark compost, 20 to 30 parts by weight of sludge, 25 to 35 parts by weight of manure for livestock, and soil improvement. A sludge fermenting fertilizer characterized by being 8 to 15 parts by weight.
【請求項4】 請求項1〜3のいずれか記載の汚泥発酵
肥料において、原材料混合物に、さらに腐敗性の有機物
質を配合することを特徴とする汚泥発酵肥料。
4. The sludge fermentation fertilizer according to any one of claims 1 to 3, wherein the raw material mixture further contains a septic organic substance.
【請求項5】 請求項4記載の汚泥発酵肥料において、
腐敗性の有機物質が、米糠、油粕、魚粉、糖蜜、及び生
ゴミから選ばれる一種以上であることを特徴とする汚泥
発酵肥料。
5. The sludge fermentation fertilizer according to claim 4,
A sludge fermenting fertilizer characterized in that the putrefactive organic substance is one or more kinds selected from rice bran, oil cake, fish meal, molasses, and garbage.
【請求項6】 請求項1〜5のいずれか記載の汚泥発酵
肥料において、原材料混合物に、さらに貝殻焼却灰を配
合することを特徴とする汚泥発酵肥料。
6. The sludge fermentation fertilizer according to any one of claims 1 to 5, wherein the raw material mixture further contains shell incineration ash.
【請求項7】 請求項1〜6のいずれか記載の汚泥発酵
肥料において、微生物が、抗酸性で乳酸を生産し酪酸を
生産せず病原性を有さずかつ拮抗価50以上である有効
微生物群であることを特徴とする汚泥発酵肥料。
7. The sludge-fermenting fertilizer according to any one of claims 1 to 6, wherein the microorganism has an antiacidity, produces lactic acid, does not produce butyric acid, has no pathogenicity, and has an antagonistic value of 50 or more. A sludge fermenting fertilizer characterized by being a group.
【請求項8】 請求項1〜7のいずれか記載の汚泥発酵
肥料において、原材料混合物に加える微生物が、ボカシ
の形態であり、前記ボカシは糖蜜を0.15〜0.25
重量%含むことを特徴とする汚泥発酵肥料。
8. The sludge fertilizer according to any one of claims 1 to 7, wherein the microorganism added to the raw material mixture is in the form of blurring, and the blurring is molasses 0.15 to 0.25.
A sludge fermenting fertilizer, which is characterized by containing wt%.
JP2001243760A 2001-08-10 2001-08-10 Sludge fertilizer Expired - Lifetime JP4875809B2 (en)

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Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006074618A1 (en) * 2005-01-07 2006-07-20 Lubos Hajek Sludge from sewage treatment plants
KR100887711B1 (en) 2007-05-31 2009-03-12 청화산영농조합법인 Seedbed soil for growing blueberry and the method for preparing thereof
CN102101797A (en) * 2009-12-22 2011-06-22 孙健 Process for producing organic fertilizer from organic wastes
CN102153393A (en) * 2011-05-06 2011-08-17 陈景河 Multielement fertilizer with marine organism calcium
CN104258808A (en) * 2014-09-02 2015-01-07 中国科学院城市环境研究所 Method and system for increasing specific surface area of sludge biochar
CN105417690A (en) * 2015-11-17 2016-03-23 仇颖超 Culture method of aerobiotic active sludge
CN106927977A (en) * 2017-04-10 2017-07-07 农业部规划设计研究院 A kind of charcoal base organic fertilizer and preparation method thereof
CN109250883A (en) * 2018-11-27 2019-01-22 内蒙古济世源环保生物科技有限公司 Method for sludge treatment
CN112608193A (en) * 2020-12-31 2021-04-06 北矿城生态科技集团有限公司 High organic matter fertilizer for desertified soil and preparation method thereof

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JPS593089A (en) * 1982-06-29 1984-01-09 三機工業株式会社 Manufacture of organic fertilizer
JPH0267392A (en) * 1988-09-01 1990-03-07 Matsui Kasei:Kk Compound soil conditioner
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Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006074618A1 (en) * 2005-01-07 2006-07-20 Lubos Hajek Sludge from sewage treatment plants
CZ308871B6 (en) * 2005-01-07 2021-07-28 K.R.K. Hájek s. r. o. Sludge from sewage treatment plants
KR100887711B1 (en) 2007-05-31 2009-03-12 청화산영농조합법인 Seedbed soil for growing blueberry and the method for preparing thereof
CN102101797A (en) * 2009-12-22 2011-06-22 孙健 Process for producing organic fertilizer from organic wastes
CN102153393A (en) * 2011-05-06 2011-08-17 陈景河 Multielement fertilizer with marine organism calcium
CN104258808A (en) * 2014-09-02 2015-01-07 中国科学院城市环境研究所 Method and system for increasing specific surface area of sludge biochar
CN105417690A (en) * 2015-11-17 2016-03-23 仇颖超 Culture method of aerobiotic active sludge
CN106927977A (en) * 2017-04-10 2017-07-07 农业部规划设计研究院 A kind of charcoal base organic fertilizer and preparation method thereof
CN109250883A (en) * 2018-11-27 2019-01-22 内蒙古济世源环保生物科技有限公司 Method for sludge treatment
CN112608193A (en) * 2020-12-31 2021-04-06 北矿城生态科技集团有限公司 High organic matter fertilizer for desertified soil and preparation method thereof

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