JP2003055077A - Fertilizer response accelerator-containing fertilizer and method of manufacturing the same - Google Patents

Fertilizer response accelerator-containing fertilizer and method of manufacturing the same

Info

Publication number
JP2003055077A
JP2003055077A JP2001246574A JP2001246574A JP2003055077A JP 2003055077 A JP2003055077 A JP 2003055077A JP 2001246574 A JP2001246574 A JP 2001246574A JP 2001246574 A JP2001246574 A JP 2001246574A JP 2003055077 A JP2003055077 A JP 2003055077A
Authority
JP
Japan
Prior art keywords
fertilizer
methane fermentation
liquid
concentrated
ultrafilter
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.)
Withdrawn
Application number
JP2001246574A
Other languages
Japanese (ja)
Inventor
Nobuo Akiyama
伸雄 秋山
Sho Hashimoto
升 橋本
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.)
NIKKI BIOSCAN CO Ltd
NIKKI-BIOSCAN CO Ltd
Original Assignee
NIKKI BIOSCAN CO Ltd
NIKKI-BIOSCAN CO Ltd
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 NIKKI BIOSCAN CO Ltd, NIKKI-BIOSCAN CO Ltd filed Critical NIKKI BIOSCAN CO Ltd
Priority to JP2001246574A priority Critical patent/JP2003055077A/en
Publication of JP2003055077A publication Critical patent/JP2003055077A/en
Withdrawn legal-status Critical Current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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Landscapes

  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)
  • Fertilizers (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method for effectively utilizing a permeated digestion liquid after ultrafiltration separation of a methane fermentation treated liquid in treating organic wastes by a methane fermentation method. SOLUTION: The method of manufacturing the fertilizer response accelerator- containing fertilizer obtaining the fertilizer response accelerator-containing fertilizer by subjecting the ultrafilter permeated digestion liquid obtained by passing the methane fermentation treated liquid of the organic wastes through the ultrafilter to thickening and drying and the fertilizer response accelerator- containing fertilizer obtained by the method.

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、畜産廃棄物などの
有機廃棄物の生物処理液を、限外濾過膜分離した後の透
過消化液から植物生育促進効果の高い肥効促進剤入り肥
料を製造する方法に関する。
TECHNICAL FIELD The present invention relates to a fertilizer containing a fertilizer, which has a high plant growth promoting effect, from a permeation digested liquid obtained by subjecting a biological treatment liquid of organic waste such as livestock waste to ultrafiltration membrane separation. It relates to a method of manufacturing.

【0002】[0002]

【従来の技術】1999年7月28日に公布された「家
畜排泄物の管理の適正化及び利用の促進に関する法律」
および2000年6月7日に公布された「食品循環資源
の再生利用の促進に関する法律」のもとで、畜産、食品
工業や家庭・レストラン・ホテルなどから排出される有
機廃棄物については適正な処理およびリサイクル利用が
求められてきている。斯かる状況のなかで、それらの有
機廃棄物を有効に処理することが可能な処理法として、
微生物による生物処理、例えばメタン発酵法などの様々
な処理法が提案され、その一部は既に実用化されてい
る。
2. Description of the Related Art "Law concerning the proper management and promotion of utilization of livestock excrement" promulgated on July 28, 1999
Under the "Promotion of Recycling of Food Recycling Resources" promulgated on June 7, 2000, it is appropriate to use organic waste emitted from livestock, the food industry, households, restaurants, hotels, etc. There is a growing demand for treatment and recycling. Under such circumstances, as a treatment method capable of effectively treating those organic wastes,
Various treatment methods such as biological treatment by microorganisms such as methane fermentation method have been proposed, and some of them have already been put to practical use.

【0003】嫌気性メタン発酵と膜分離技術を巧みに組
み合わせ、有機廃棄物を効果的に処理するバイオレック
(BIOREK)プロセスと称される技術がデンマークのバイ
オスキャン社によって開発されている(WO99/42
423参照)。このバイオレックプロセスは、有機性廃
棄物をメタン発酵槽中で嫌気的メタン発酵し、生成する
メタンガスを主成分とするバイオガスから電力と熱エネ
ルギーを回収する一方、メタン発酵後の消化液は、アン
モニアおよびCO2を分離した後、逆浸透膜を用いて浄
水と、低濃度ながら肥料成分である窒素、リン(P
25)及びカリ(K 2O)を含む液とに分離回収され
る。このプロセスは1997年よりデンマークやドイツ
で既に商業規模の操業が実施されており、その他世界の
主要国でプラントの建設や建設計画が進行中である。
Skillfully combined anaerobic methane fermentation and membrane separation technology
Biorec, which combines and effectively treats organic waste
The technology called (BIOREK) process is used in Denmark
Developed by OSCAN (WO99 / 42
423). This Biorec process is an organic waste
Anaerobic methane fermentation of wastes in a methane fermenter to produce
Power and heat energy from biogas, which is mainly composed of methane gas
While the rugie is recovered, the digestive juice after methane fermentation is
Monia and CO2After separation, clean with a reverse osmosis membrane.
Water and nitrogen, phosphorus (P
2OFive) And potassium (K 2O) and the liquid containing
It This process has been used in Denmark and Germany since 1997.
Is already in commercial operation in
Plant construction and construction plans are underway in major countries.

【0004】[0004]

【発明が解決しようとする課題】ところで、このプロセ
スでスチーム加熱などによって消化液より分離されるア
ンモニア及びCO2は、それらを含む水溶液として回収
されるが、同時に原料として供給される有機性廃棄物に
もとづく臭気も含まれ、そのままの状態で窒素肥料の原
料として使用することは好まれない。以下に、豚の糞尿
をこのバイオレックプロセスで処理した場合に得られる
該液の組成分析の一例を示す。 NH3: 50000mg/L CO2: 58700mg/L
By the way, ammonia and CO 2 separated from the digestive juice by steam heating or the like in this process are recovered as an aqueous solution containing them, but at the same time, the organic wastes supplied as raw materials are discharged. It also contains an odor based on it, and it is not preferred to use it as it is as a raw material for nitrogen fertilizer. The following is an example of the composition analysis of the liquid obtained when pig manure is treated by this Biorec process. NH 3: 50000mg / L CO 2 : 58700mg / L

【0005】また、このプロセスで逆浸透膜によって浄
水と分離されて回収される残液は、西欧ではそのまま液
肥として使用されているが、該残液にふくまれる窒素、
リン酸、カリは希薄であり、降雨量が多い我が国では液
肥として使用するメリットは少ない。以下に、豚の糞尿
をこのバイオレックプロセスで処理した場合に得られる
該残液の組成分析の一例を示す。 N: 0.02重量% P25: 0.82重量% K2O: 1.68重量% 有機成分:0.81重量% pH: 8.0
The residual liquid separated from the purified water by the reverse osmosis membrane and collected in this process is used as it is as liquid fertilizer in Western Europe, but the nitrogen contained in the residual liquid,
Phosphoric acid and potassium are dilute, and there is little merit in using them as liquid fertilizer in Japan, which has a large amount of rainfall. An example of the composition analysis of the residual liquid obtained when pig manure is treated by this Biorec process is shown below. N: 0.02 wt% P 2 O 5: 0.82 wt% K 2 O: 1.68 wt% organic component: 0.81 wt% pH: 8.0

【0006】本発明は前記事情に鑑みてなされたもの
で、前記バイオレックプロセスにおいて、メタン発酵処
理液を限外濾過膜分離(ウルトラフィルター分離)した
後の透過消化液の有効利用法の提供を目的としている。
The present invention has been made in view of the above circumstances, and provides a method for effectively using a permeation digestive liquid after ultrafiltration membrane separation (ultra filter separation) of a methane fermentation treatment liquid in the Biorec process. Has an aim.

【0007】[0007]

【課題を解決するための手段】本発明者らは、前記メタ
ン発酵後の処理液を限外濾過膜分離した後の透過消化液
の有効利用法について鋭意研究を重ねた結果、該透過消
化液を直接低温で濃縮粉末化した製品を施肥した土壌
と、該製品に含まれる量と同等の量の窒素(N)、リン
酸(P25)およびカリ(K2O)を含有する通常の無
機肥料を施肥した土壌とを比較して植物栽培試験を行っ
た結果、該製品を施肥した土壌で栽培した植物の生育が
顕著に促進されることを知見し、本発明を完成させた。
Means for Solving the Problems The inventors of the present invention have conducted extensive studies as to the effective use of permeated digestive liquid after ultrafiltration membrane separation of the treated liquid after the methane fermentation, and as a result, the permeated digested liquid has been obtained. Soil fertilized with a product obtained by concentrating and powdering directly at low temperature, and usually containing nitrogen (N), phosphoric acid (P 2 O 5 ) and potassium (K 2 O) in an amount equivalent to that contained in the product. As a result of performing a plant cultivation test in comparison with the soil fertilized with the above-mentioned inorganic fertilizer, it was found that the growth of the plant cultivated in the soil fertilized with the product was remarkably promoted, and the present invention was completed.

【0008】即ち、本発明は、有機廃棄物のメタン発酵
処理液をウルトラフィルターに通して得られるウルトラ
フィルター透過消化液を、濃縮・乾燥して肥効促進剤を
含む肥料を得ることを特徴とする肥効促進剤入り肥料の
製造方法を提供する。この製造方法において、濃縮・乾
燥する前の消化液に無機酸を加えること、及び消化液を
濃縮・乾燥する際に、該液を減圧蒸発濃縮装置によって
濃縮液とし、次いで該濃縮液を噴霧乾燥装置によって粉
末に乾燥すること、及びこれらの濃縮・乾燥を80℃以
下の温度で行うことが望ましい。また、本発明は前記の
製造方法により得られた肥効促進剤入り肥料を提供す
る。この肥効促進剤入り肥料は、さらに少なくとも1種
の肥料成分を混合しても良い。
That is, the present invention is characterized in that an ultrafilter-permeated digested liquid obtained by passing a methane fermentation treatment liquid of organic waste through an ultrafilter is concentrated and dried to obtain a fertilizer containing a fertilizer. Provided is a method for producing a fertilizer containing a fertilizer. In this manufacturing method, when an inorganic acid is added to the digestive juice before being concentrated and dried, and when the digested juice is concentrated and dried, the solution is made into a concentrated solution by a vacuum evaporation concentration device, and then the concentrated solution is spray-dried. Desirably, the powder is dried by an apparatus, and the concentration and drying thereof are performed at a temperature of 80 ° C. or lower. The present invention also provides a fertilizer containing a fertilizer, which is obtained by the above-mentioned production method. This fertilizer containing a fertilizer effect promoter may be further mixed with at least one fertilizer component.

【0009】[0009]

【発明の実施の形態】本発明による肥効促進剤入り肥料
は、有機廃棄物のメタン発酵後の消化液から得られ、窒
素(N)、リン酸(P25)、カリ(K2O)などの肥
料成分と、肥効促進効果を有している有機物(肥効促進
剤という)とを含んでいる。この肥効促進剤は、明確な
構造、組成は未だ明確でないが、分子量1000以下の
比較的低分子量の物質を多く含む組成物であること、及
び肥料と共に植物に与えると、肥料のみを与えて栽培し
たものよりも格段に生長を促進し得る、といった特徴を
有している。
BEST MODE FOR CARRYING OUT THE INVENTION A fertilizer containing a fertilizer promoter according to the present invention is obtained from a digested liquid of an organic waste after methane fermentation, and contains nitrogen (N), phosphoric acid (P 2 O 5 ), potassium (K 2 O) and other fertilizer components, and an organic substance having a fertilizer effect-promoting effect (called a fertilizer promoter). This fertilizer enhancer has a clear structure and composition, but it is a composition containing a large amount of relatively low molecular weight substances having a molecular weight of 1000 or less, and when given to plants together with fertilizers, only fertilizers are given. It has the feature that it can promote growth much more than cultivated ones.

【0010】一般に、この種の有機廃棄物の処理液中に
含有され、且つ肥効促進効果を有するものは、総じて腐
植酸であるとされている。概して腐植酸は、土壌中で生
物遺体が微生物により分解された後、自発的に重合した
有機高分子であるとされ、1950年代よりソ連の研究
者を中心に精力的に検討が行われ、その構造は複雑な環
状芳香族核のまわりに線状に重合した炭素側鎖を持つか
なり高分子量(約2000程度)の物質であるとされて
いる。
Generally, humic acid is generally contained in the treatment liquid of this type of organic waste and has a fertilizing effect promoting effect. Generally, humic acid is said to be an organic polymer that spontaneously polymerizes after biological bodies are decomposed by microorganisms in soil. Since the 1950s, soviet researchers have been vigorously studied and studied. The structure is believed to be a fairly high molecular weight (approximately 2000) material with linearly polymerized carbon side chains around a complex cyclic aromatic nucleus.

【0011】一方、本発明に係る肥効促進剤の分子量分
布をゲルクロマトグラフィーで測定した結果、その分子
量分布は以下の如くであり、前述した腐植酸に比較して
かなり低分子量の物質を主成分としていた。従って本発
明に係る肥効促進剤は腐植酸とは異なる物質である。 分子量 組成比 200以下 45.9% 200−1000 39.2% 1000−6000 12.1% 6000以上 2.8%
On the other hand, as a result of measuring the molecular weight distribution of the fertilizer promoting agent according to the present invention by gel chromatography, the molecular weight distribution is as shown below, and the substance having a considerably low molecular weight as compared with the above-mentioned humic acid is mainly used. It was an ingredient. Therefore, the fertilizer promoter according to the present invention is a substance different from humic acid. Molecular weight Composition ratio 200 or less 45.9% 200-1000 39.2% 1000-6000 12.1% 6000 or more 2.8%

【0012】この肥効促進剤は、有機廃棄物のメタン発
酵後の消化液を濃縮・乾燥することによって、肥料成分
(窒素、リン酸およびカリ)とともに、肥効促進剤入り
肥料として得られる。以下、本発明に係る肥効促進剤入
り肥料の製造方法の一形態を図面を参照して説明する。
This fertilizer is obtained as a fertilizer containing a fertilizer together with fertilizer components (nitrogen, phosphoric acid and potassium) by concentrating and drying the digested liquid of the organic waste after methane fermentation. Hereinafter, one embodiment of a method for producing a fertilizer containing a fertilizer accelerating agent according to the present invention will be described with reference to the drawings.

【0013】図1は、本発明の肥効促進剤入り肥料の製
造方法の一形態を説明するための製造プロセスを例示す
る図である。本製造プロセスは、有機廃棄物を嫌気的に
メタン発酵するためのメタン発酵槽1と、該メタン発酵
槽1からの消化液から水とともにメタン細菌より小さい
成分を透過分離するウルトラフィルター2と、該ウルト
ラフィルター2を透過した消化液に無機酸を添加して、
含有するアンモニアをアンモニウム塩溶液にするアンモ
ニア固定槽3と、該装置3よりの消化液を濃縮する減圧
蒸発濃縮装置4と、該装置4から得られる濃縮液を噴霧
乾燥する噴霧乾燥装置5とを主要な構成要素として備え
ている。以下、このプロセスを用いて肥効促進剤入り肥
料を製造する各工程を説明する。
FIG. 1 is a diagram illustrating a manufacturing process for explaining one embodiment of a method for manufacturing a fertilizer containing a fertilizer effect enhancer of the present invention. The present manufacturing process comprises a methane fermentation tank 1 for anaerobically methane fermenting organic waste, an ultrafilter 2 for permeating and separating components smaller than methane bacteria together with water from a digested liquid from the methane fermentation tank 1, Add an inorganic acid to the digestive juice that has passed through the Ultra Filter 2,
An ammonia fixing tank 3 for converting the contained ammonia into an ammonium salt solution, a vacuum evaporation concentration device 4 for concentrating the digested liquid from the device 3, and a spray drying device 5 for spray-drying the concentrated liquid obtained from the device 4. It is provided as a main component. Hereinafter, each step of producing a fertilizer containing a fertilizer promoting agent using this process will be described.

【0014】(1)メタン発酵工程 メタン発酵工程では、各種の有機廃棄物をメタン発酵槽
1内に供給し、槽内でメタン生成細菌(例えばMethanoc
occus属細菌,Methanosarcina属細菌,Methanobacteriu
m属細菌など)によって有機廃棄物を嫌気的メタン発酵
し、メタンガスを主成分とするバイオガスを発生させ
る。このメタン発酵のために用いられる発酵槽は、基本
的には従来より周知の嫌気的培養槽を適用することがで
き、操業規模に応じて各種のタンク式培養槽等を用いる
ことができる。本例示においてメタン発酵槽1には、有
機廃棄物を供給する供給ラインと、発生したバイオガス
を槽外に取り出すバイオガス取出ラインと、消化液をウ
ルトラフィルター2に供給する消化液供給ラインと、槽
内の余剰固形物(ブリード)を取り出すブリード取出ラ
インとを備えている。さらにこのメタン発酵槽1には、
撹拌装置、保温装置、酸あるいはアルカリを添加して発
酵液のpHを調節するためのpH調整装置などの各種装
置を付設し得る。
(1) Methane Fermentation Process In the methane fermentation process, various organic wastes are fed into the methane fermentation tank 1 and methane-producing bacteria (eg Methanoc) are supplied in the tank.
occus spp, Methanosarcina spp, Methanobacteriu
Anaerobic methane fermentation of organic waste by m bacteria, etc., to generate biogas with methane gas as the main component. As a fermenter used for this methane fermentation, an anaerobic culture tank known in the related art can be basically applied, and various tank-type culture tanks and the like can be used depending on the operation scale. In this example, the methane fermentation tank 1 has a supply line for supplying organic waste, a biogas extraction line for taking out generated biogas out of the tank, and a digestive liquid supply line for supplying digestive liquid to the ultrafilter 2. A bleed take-out line for taking out excess solid matter (bleed) in the tank is provided. Furthermore, in this methane fermentation tank 1,
Various devices such as a stirring device, a heat retaining device, and a pH adjusting device for adjusting the pH of the fermentation liquid by adding an acid or an alkali may be attached.

【0015】このメタン発酵槽1に供給される有機廃棄
物は、メタン生成細菌によってメタン発酵が可能な有機
物を含むものであれば、特に限定されず、例えば豚、牛
の糞尿、鶏糞などの畜産業から排出される有機廃棄物、
あるいは一般家庭、レストラン、ホテル、食品工場など
からの廃棄食品、生ゴミ類などである。これらの有機廃
棄物をメタン発酵槽1に供給する場合、必要に応じて加
水し、有機廃棄物を沈殿槽に入れて砂や砂利等を分離
し、さらに破砕機にかけて粗大物を細かく粉砕し、さら
に必要に応じて難分解物を沈殿させて分離したり、篩
(スクリーン)を通して難分解物を捕集する前処理を行
って良い。さらに、有機廃棄物を中和するため、硫酸な
どの酸あるいは石灰乳などのアルカリを添加しても良
い。なお、分離除去した難分解物はコンポスト生産に利
用し得る。前処理された有機廃棄物は、供給ラインを通
してメタン発酵槽1内に供給される。
The organic waste supplied to the methane fermentation tank 1 is not particularly limited as long as it contains organic matter that can be methane fermented by methanogenic bacteria. For example, livestock such as pig and cow manure and chicken manure. Organic waste emitted from industry,
Alternatively, it is waste food, kitchen waste, etc. from ordinary households, restaurants, hotels, food factories and the like. When supplying these organic wastes to the methane fermentation tank 1, water is added as necessary, the organic wastes are placed in a settling tank to separate sand, gravel, etc., and a crusher is used to finely pulverize coarse materials, Further, if necessary, the hardly decomposable substance may be precipitated and separated, or a pretreatment for collecting the hardly decomposable substance through a screen may be performed. Further, in order to neutralize the organic waste, an acid such as sulfuric acid or an alkali such as lime milk may be added. The difficult-to-decompose substance separated and removed can be used for compost production. The pretreated organic waste is supplied into the methane fermentation tank 1 through a supply line.

【0016】メタン発酵において、メタン発酵槽1内は
嫌気性雰囲気に保ち、発生するバイオガスをバイオガス
取出ラインを通して取り出す。メタン発酵槽1内は、中
温発酵菌を用いる場合には20〜40℃、好ましくは3
5〜37℃程度に、高温発酵菌を用いる場合には50〜
60℃、好ましくは55〜57℃に保温する。メタン発
酵槽1内でのメタン発酵は、バッチ式、半連続式あるい
は連続式とすることができる。本例示では、消化液を抜
き出してウルトラフィルター2にかけて、該フィルター
を透過しない未分解有機物とメタン生成細菌をメタン発
酵槽1に返送することができるので、単一の発酵槽を用
いて連続発酵を行うことが可能である。なお、半連続式
または連続式メタン発酵を行う場合には、メタン発酵槽
1を複数基用意し、あるいは1基の槽内を複数に区画
し、発酵液を別な槽に移動させながら発酵を進めること
もできる。メタン発酵の継続時間は、有機廃棄物の有機
物濃度、発酵温度によって適宜選択し得るが、例えば豚
の糞尿を用い、中温発酵菌によって37℃でメタン発酵
を行う場合、滞留時間は9〜11日程度とすることが望
ましい。
In the methane fermentation, the inside of the methane fermentation tank 1 is kept in an anaerobic atmosphere, and the generated biogas is taken out through the biogas taking line. The inside of the methane fermentation tank 1 is 20 to 40 ° C. when using a mesophilic fermentation bacterium, preferably 3
5 to 37 ° C, 50 to 50 when using high temperature fermenting bacteria
The temperature is kept at 60 ° C, preferably 55 to 57 ° C. The methane fermentation in the methane fermentation tank 1 can be batch type, semi-continuous type or continuous type. In this example, the digested liquid is extracted and applied to the ultrafilter 2, and undecomposed organic matter and methanogenic bacteria that do not pass through the filter can be returned to the methane fermentation tank 1, so that continuous fermentation is performed using a single fermentation tank. It is possible to do. When performing semi-continuous or continuous methane fermentation, multiple methane fermentation tanks 1 are prepared, or the inside of one tank is divided into a plurality of tanks, and fermentation is performed while moving the fermented liquid to another tank. You can also proceed. The duration of the methane fermentation can be appropriately selected depending on the organic matter concentration of the organic waste and the fermentation temperature. For example, when methane fermentation is carried out at 37 ° C. with mesophilic fermentation bacteria using pig manure, the residence time is 9 to 11 days. It is desirable to set the degree.

【0017】メタン発酵で発生するバイオガスは、メタ
ンガス(約72〜74容量%)を主成分とし、その他C
2(約20〜25容量%)、H2、H2S、N2などが含
まれる。バイオガス取出ラインを通してメタン発酵槽1
から取り出されるバイオガスは、ガスホルダーに貯留し
ておき、H2Sなどの有害成分を除去した後、燃料等と
して利用される。例えば、このバイオガスを複合ガス発
電機(コ・ジェネ装置)やガスタービンの燃料とするこ
とによって電気、熱(温水)を得ることができる。ある
いは、バイオガスをリフォーマーで処理し、得られる水
素ガスを燃料電池の燃料として発電することもできる。
Biogas generated in methane fermentation is mainly composed of methane gas (about 72 to 74% by volume), and other C
O 2 (about 20 to 25% by volume), H 2 , H 2 S, N 2 and the like are included. Methane fermentation tank 1 through the biogas extraction line
The biogas extracted from the gas is stored in a gas holder, and after removing harmful components such as H 2 S, it is used as fuel or the like. For example, electricity and heat (hot water) can be obtained by using this biogas as a fuel for a combined gas generator (co-generator) or a gas turbine. Alternatively, biogas can be treated with a reformer, and the resulting hydrogen gas can be used as fuel for a fuel cell to generate electricity.

【0018】メタン発酵を継続して行うと、メタン発酵
槽1内に余剰固形物(ブリード)が溜まってくる。この
ブリードは定期的に、もしくは槽内のブリード貯留量が
予め設定した基準を超えた時点で、ブリード取出ライン
を通してメタン発酵槽1外に取り出される。取り出され
たブリードは、コンポスト生産に利用し得る。
When methane fermentation is continuously carried out, excess solid matter (bleed) is accumulated in the methane fermentation tank 1. The bleed is taken out of the methane fermentation tank 1 through the bleed take-out line at regular intervals or when the amount of stored bleed in the tank exceeds a preset standard. The removed bleed can be used for compost production.

【0019】(2)ウルトラフィルター分離工程 メタン発酵槽1内でメタン発酵を終えた消化液は、消化
液供給ラインを通してウルトラフィルター2に供給され
る。ウルトラフィルター2は、メタン生成細菌(例えば
0.1〜10μm程度)や未分解有機物を透過せず、水
及び低分子量の発酵分解物を透過するような微細孔を有
している。
(2) Ultra Filter Separation Step The digested liquid that has undergone methane fermentation in the methane fermentation tank 1 is supplied to the ultra filter 2 through the digested liquid supply line. The ultrafilter 2 has fine pores that do not allow methanogenic bacteria (for example, about 0.1 to 10 μm) and undecomposed organic matter to permeate but water and low-molecular-weight fermentation decomposed matter.

【0020】このウルトラフィルター2によって消化液
を膜分離し、低分子量の発酵分解物を含む水を透過して
抜き出すとともに、返送ラインを通してフィルター2を
透過しないメタン生成細菌と未分解有機物を含む液をメ
タン発酵槽1に返送する。このようにメタン生成細菌と
未分解有機物をメタン発酵槽1に返送することによっ
て、メタン生成細菌と未分解有機物の流出を防ぎ、発酵
槽中の有機物とメタン生成細菌を高濃度に保つことが可
能となり、その結果有機廃棄物の発酵効率を向上させる
ことができる。
The digestion liquid is membrane-separated by this ultra filter 2, water containing low-molecular-weight fermentation decomposition products is permeated and extracted, and a liquid containing methanogenic bacteria and undecomposed organic substances that do not permeate the filter 2 through the return line. Return to methane fermentation tank 1. By returning the methanogenic bacteria and undecomposed organic matter to the methane fermentation tank 1 in this way, it is possible to prevent the outflow of methanogenic bacteria and undecomposed organic matter and keep the organic matter and methanogenic bacteria in the fermenter at high concentrations. As a result, the fermentation efficiency of organic waste can be improved.

【0021】ウルトラフィルター2の運転圧力は2〜1
0気圧、好ましくは4〜7気圧程度とされる。ウルトラ
フィルター2の運転圧を高くすることによって、ウルト
ラフィルター2透過液中の溶存CO2濃度を高くするこ
とができ、メタン発酵槽1内のCO2を該透過液中に追
い出すことができるので、結果的としてメタン発酵槽1
から得られるバイオガス中のメタンガス濃度を高くする
ことができる。
The operating pressure of the ultrafilter 2 is 2 to 1
The pressure is 0 atm, preferably about 4 to 7 atm. By increasing the operating pressure of the ultrafilter 2, the dissolved CO 2 concentration in the permeate of the ultrafilter 2 can be increased, and the CO 2 in the methane fermentation tank 1 can be expelled into the permeate. As a result, methane fermenter 1
It is possible to increase the methane gas concentration in the biogas obtained from

【0022】(3)アンモニア固定工程 ウルトラフィルター2を透過した浄化液は、次に、アン
モニア固定槽3に供給され、該消化液に含まれているア
ンモニアが、後述する(4)濃縮・乾燥工程にて揮散さ
れないように、無機酸の添加によってアンモニアをアン
モニウム塩溶液として固定する。ここで、アンモニアの
揮散防止のために添加する無機酸の量は、製品としての
肥効促進剤入り肥料の使用目的に応じて任意に選択し得
る。この消化液への無機酸の添加は、アンモニア固定槽
3のなかで撹拌機を用いて消化液を撹拌しながら常温で
添加するが、その際消化液中に含まれる溶存CO2の一
部が気化され放散する。
(3) Ammonia-fixing step The purified liquid that has passed through the ultrafilter 2 is then supplied to the ammonia-fixing tank 3 so that ammonia contained in the digestive liquid will be described later in (4) Concentration / drying step. The ammonia is fixed as an ammonium salt solution by the addition of an inorganic acid so as not to be volatilized. Here, the amount of the inorganic acid added to prevent the volatilization of ammonia can be arbitrarily selected according to the purpose of use of the fertilizer containing a fertilizer as a product. The inorganic acid is added to the digestive juice at room temperature while stirring the digestive juice in the ammonia fixing tank 3 using a stirrer. At that time, some of the dissolved CO 2 contained in the digestive juice is added. It vaporizes and dissipates.

【0023】この消化液に添加する無機酸としては、塩
酸、硫酸、硝酸、リン酸等各種の無機酸を使用すること
ができるが、好ましくはリン酸及び硫酸が使用される。
塩酸を使用した場合は製品としての肥効促進剤入り肥料
を土壌に施肥した場合、土壌の電気伝導度(EC)の上
昇を招くのみならず、土壌中の塩素イオンの存在は農作
物の生育上好ましくなく、また、硝酸の使用は生成され
る硝酸アンモニウムの土壌中での流亡による河川や地下
水の硝酸含有量の増加などを招き、環境汚染上好ましく
ない。無機酸としてリン酸や硫酸を使用した場合は、消
化液中に肥効上好ましいリン酸アンモニウム(リン安)
や硫酸アンモニウム(硫安)が生成される。
Various inorganic acids such as hydrochloric acid, sulfuric acid, nitric acid and phosphoric acid can be used as the inorganic acid added to the digestive juice, but phosphoric acid and sulfuric acid are preferably used.
When hydrochloric acid is used, when fertilizer containing a fertilizer as a product is applied to the soil, not only does the electrical conductivity (EC) of the soil increase, but the presence of chloride ions in the soil also affects the growth of crops. It is not preferable, and use of nitric acid is not preferable in terms of environmental pollution because it causes increase of nitric acid content in rivers and groundwater due to runoff of generated ammonium nitrate in soil. When phosphoric acid or sulfuric acid is used as the inorganic acid, ammonium phosphate (phosphorus ammonium) is preferable in the digestive juice for fertilizing effect.
Ammonium sulfate (ammonium sulfate) is produced.

【0024】(4)濃縮・乾燥工程 この工程では、前記アンモニア固定工程で無機酸を添加
した消化液を減圧蒸発濃縮装置4で濃縮し、さらに該濃
縮液を噴霧乾燥機5で乾燥し、粉末状の肥効促進剤入り
肥料(粉末肥料)を製造する。
(4) Concentration / Drying Step In this step, the digested liquid to which the inorganic acid has been added in the ammonia fixing step is concentrated by the vacuum evaporation concentration device 4, and the concentrated liquid is dried by the spray dryer 5 to obtain a powder. Manufacture fertilizer (powder fertilizer) containing fertilizer.

【0025】前記消化液を常圧下で加熱して濃縮を行う
と、加熱温度を高くせざるを得ず、該液中に残存してい
るCO2並びに含まれている有機物の分解による発泡が
甚だしく、効率よく濃縮を行うことは難しく、また同時
に有用な有機物(肥効促進剤)の分解による損失につな
がる。
When the digestion solution is heated under atmospheric pressure to be concentrated, the heating temperature is inevitably raised, and the CO 2 remaining in the solution and the foaming due to the decomposition of the organic matter contained therein are serious. However, it is difficult to perform efficient concentration, and at the same time, it leads to loss due to decomposition of useful organic substances (fertility promoters).

【0026】そこで、本発明の肥効促進剤入り肥料の製
造方法にあっては、先ず減圧蒸発濃縮を行い、次いで噴
霧乾燥法による粉末化を、それぞれ蒸発乾燥温度をなる
べく低目(望ましくは、減圧蒸発濃縮にあっては60℃
以下、また噴霧乾燥にあっては80℃以下)に設定して
行うことにより、溶存CO2の緩やかな放出と、有効な
有機成分の分解による損失を防いで、該消化液中に含ま
れる肥料成分と共に肥効促進剤を乾燥し、肥効性の高い
粉末肥料を製造する。さらに、該消化液中に存在する有
機物の分解のおそれを完全に除く観点から、噴霧乾燥法
に代えて凍結乾燥方式を採用することもできる。またさ
らに別な方法として、前記アンモニア固定工程で無機酸
を添加した消化液または減圧蒸発濃縮装置4で濃縮した
濃縮液を、回転式動転造粒装置等の造粒装置に入れ、造
粒しながら熱風乾燥することもできる。
Therefore, in the method for producing a fertilizer containing a fertilizer accelerating agent of the present invention, first, evaporation under reduced pressure is carried out, and then pulverization by a spray drying method is carried out at a low evaporation drying temperature (preferably, 60 ° C for vacuum evaporation
Hereinafter, in spray drying, the temperature is set to 80 ° C. or lower) to prevent the gradual release of dissolved CO 2 and the loss due to the decomposition of effective organic components, and to make a fertilizer contained in the digestive juice. The fertilizer is dried together with the ingredients to produce a highly fertile powder fertilizer. Furthermore, from the viewpoint of completely eliminating the risk of decomposition of organic substances present in the digestive juice, a freeze-drying method can be adopted instead of the spray-drying method. As still another method, the digestive liquid to which the inorganic acid is added in the ammonia fixing step or the concentrated liquid concentrated in the vacuum evaporation / concentration device 4 is put into a granulating device such as a rotary tumbling granulating device and granulated. It can be dried with hot air.

【0027】この減圧蒸発濃縮において、該消化液を例
えば10倍に濃縮することは極めて容易であり、有機物
の分解による発泡現象も全く認められず、無色透明で無
臭の蒸留凝縮水とともに、濃縮液が得られる。
In this evaporation under reduced pressure, it is extremely easy to concentrate the digested liquid to, for example, 10 times, no foaming phenomenon due to decomposition of organic substances is observed, and the concentrated liquid is condensed with colorless and transparent odorless distilled condensed water. Is obtained.

【0028】また、噴霧乾燥法によって得られる肥効促
進剤入り肥料(粉末肥料)は、極めて微細な粉末状(粉
末の粒子径は約20μm)のものであり、乾燥において
噴霧乾燥機のノズルの開閉など操作上のトラブルを発生
することなく乾燥化が可能である。
The fertilizer containing fertilizer promoter (powder fertilizer) obtained by the spray drying method is in the form of extremely fine powder (the particle diameter of the powder is about 20 μm), and the nozzle of the spray dryer is used for drying. It is possible to dry without causing operational troubles such as opening and closing.

【0029】なお、原料の有機廃棄物およびメタン発酵
槽中の微生物類は、消化液をウルトラフィルター2を透
過させること、およびその後の減圧蒸発濃縮工程、およ
び常圧噴霧乾燥工程での熱風との接触によって完全に滅
菌され、衛生上何ら問題とならない。
It should be noted that the organic waste as a raw material and the microorganisms in the methane fermentation tank are mixed with the hot air in the digestion solution permeating through the ultrafilter 2 and the subsequent vacuum evaporation concentration step and atmospheric pressure spray drying step. It is completely sterilized by contact and does not cause any problems in hygiene.

【0030】以上のように、この肥効促進剤入り肥料の
製造方法によれば、家畜排泄物を含む有機廃棄物のメタ
ン発酵後の消化液から、肥効促進効果のある有機物(肥
効促進剤)及び肥料成分を殆ど損失することなく、取り
扱い容易な且つ肥効性のある粉末状の肥料とすることが
でき、有機廃棄物処理にまつわる資源リサイクル利用の
問題、特にメタン発酵後の消化液の有効利用に関する問
題を一挙に解決することができる。
As described above, according to the method for producing a fertilizer containing a fertilizer, a digestive liquid after methane fermentation of an organic waste containing livestock excrement produces an organic substance having a fertilizer promoting effect (facilitator Agent and fertilizer components are hardly lost, and it is possible to make a powdery fertilizer that is easy to handle and has a fertile effect, and the problem of resource recycling utilization related to the treatment of organic wastes, especially the digestive liquid after methane fermentation. It is possible to solve all problems related to effective use at once.

【0031】本発明の別な形態は、この肥効促進剤入り
肥料に、少なくとも1種の肥料を混合した肥効促進剤入
り肥料である。混合される肥料は、従来より周知の各種
肥料、例えば、第1種複合肥料(配合肥料、化成肥
料)、第2種複合肥料、第3種複合肥料、発酵廃液乾燥
複合肥料、ペースト肥料、液状複合肥料などの複合肥
料、硫安や尿素などの窒素質肥料、過リン酸石灰や熔成
リン肥などのリン酸質肥料、硫酸カリや塩化カリなどの
カリ質肥料、有機質肥料、石灰質肥料、ケイ酸や苦土を
含む特殊化成肥料、微量要素複合肥料、葉面散布肥料、
農薬入肥料などを挙げることができる。
Another embodiment of the present invention is a fertilizer containing a fertilizer, wherein at least one fertilizer is mixed with the fertilizer containing a fertilizer. The fertilizers to be mixed are various well-known fertilizers, for example, type 1 compound fertilizers (combined fertilizers, chemical fertilizers), type 2 compound fertilizers, type 3 compound fertilizers, fermentation waste liquid dry compound fertilizers, paste fertilizers, liquids. Compound fertilizers such as compound fertilizers, nitrogenous fertilizers such as ammonium sulfate and urea, phosphate fertilizers such as lime superphosphate and fused phosphorus fertilizer, potash fertilizers such as potassium sulfate and potassium chloride, organic fertilizers, calcareous fertilizers, silica Specialized chemical fertilizer containing acid and magnesia, trace element compound fertilizer, foliar spray fertilizer,
Pesticide-containing fertilizer can be used.

【0032】この肥効促進剤入り肥料に含まれる肥料成
分、特にリン酸(P25)成分は、前記(3)アンモニ
ア固定工程において使用する無機酸の種類により、その
含有量が大きく変化される。例えば、アンモニアの固定
にリン酸を使用した場合は、肥料中にリン酸アンモニウ
ムの形態のリン酸(P25)が多く含まれる。従って、
この肥効促進剤入り肥料の使用量は、該肥料の肥料成分
含有量、栽培する農作物の種類、栽培方法、栽培時期や
土壌の種類と状態、肥料施用法などによって適宜選択さ
れる。以下、実施例により本発明の効果を実証する。
The content of fertilizer components, particularly phosphoric acid (P 2 O 5 ) component, contained in the fertilizer containing the fertilizer promoter greatly varies depending on the type of the inorganic acid used in the step (3) ammonia fixing step. To be done. For example, when phosphoric acid is used to fix ammonia, the fertilizer contains a large amount of phosphoric acid (P 2 O 5 ) in the form of ammonium phosphate. Therefore,
The amount of the fertilizer containing the fertilizer promoting agent used is appropriately selected depending on the fertilizer component content of the fertilizer, the type of agricultural crop to be cultivated, the cultivation method, the cultivation time and the type and state of soil, the fertilizer application method, and the like. Hereinafter, the effects of the present invention will be demonstrated by examples.

【0033】[0033]

【実施例】実施例1:肥効促進剤入り肥料の製造 図1に示す製造プロセスにより、豚の糞尿をメタン発酵
処理し、消化液から本発明に係る肥効促進剤入り肥料を
製造した。ウルトラフィルター2を透過した消化液7
7.4kgに肥料用リン酸液(P25、52%濃度)を
2.33kg添加して該液に含まれているアンモニアを
リン酸アンモニウム溶液とした液78.6kgを(株)
大川原製作所製の遠心式薄膜真空蒸発濃縮装置に供給
し、加熱温度110℃、蒸発温度50℃、真空度12k
paにて蒸発濃縮を行い、6.9kgの濃縮液を得た。
次いで、この濃縮液2.3kgを大川原化工機(株)製
の噴霧乾燥機(熱風:120℃、乾燥温度:60℃)に
供給し、何等問題なく1.06kgの肥効促進剤入り肥
料(本発明粉末肥料−1)を得た。
EXAMPLES Example 1: Manufacture of fertilizer containing fertilizer, fertilizer containing pig fertilizer according to the present invention was produced from digestive juice by subjecting pig manure to methane fermentation treatment. Digestive fluid 7 that has passed through the ultrafilter 2
2.34 kg of a phosphoric acid solution for fertilizer (P 2 O 5 , 52% concentration) was added to 7.4 kg to prepare 78.6 kg of a liquid containing ammonia as an ammonium phosphate solution.
It is supplied to a centrifugal thin film vacuum evaporative concentrator manufactured by Okawara Seisakusho, with a heating temperature of 110 ° C, an evaporation temperature of 50 ° C, and a vacuum degree of 12k.
Evaporation and concentration were carried out with pa to obtain 6.9 kg of concentrated liquid.
Next, 2.3 kg of this concentrated liquid was supplied to a spray dryer (hot air: 120 ° C., drying temperature: 60 ° C.) manufactured by Okawara Kakohki Co., Ltd., and 1.06 kg of a fertilizer containing a fertilizer promoting agent without any problem ( The present invention powder fertilizer-1) was obtained.

【0034】また、上記ウルトラフィルター2を透過し
た消化液58.6kgに硫酸(H2SO4,98%含有)
を1.1kg添加して該液に含まれているアンモニアを
硫酸アンモニウム溶液とした液58.9kgを上記の遠
心式薄膜真空蒸発濃縮装置に供給し、上記と同様な操作
条件のもとで蒸発濃縮を行い、5.2kgの濃縮液を得
た。次いでこの濃縮液1.7kgを上記の噴霧乾燥機に
供給し、上記と同様な操作条件のもとで噴霧乾燥を行
い、0.81kgの肥効促進剤入り肥料(本発明粉末肥
料−2)を得た。
In addition, 58.6 kg of digestive fluid that has passed through the ultrafilter 2 is mixed with sulfuric acid (containing H 2 SO 4 , 98%).
Was added to the above centrifugal thin-film vacuum evaporative concentrator to evaporate and condense under the same operating conditions as above. Then, 5.2 kg of concentrated liquid was obtained. Next, 1.7 kg of this concentrated liquid was supplied to the above spray dryer, spray-dried under the same operating conditions as described above, and 0.81 kg of a fertilizer containing a fertilizer accelerating agent (the present powdered fertilizer-2). Got

【0035】表1に、アンモニア固定にリン酸液を使用
した場合(本発明粉末肥料−1の製造)と、アンモニア
固定固定に硫酸を使用した場合(本発明粉末肥料−2の
製造)の図1中符号〜に示す各工程での物質収支を
示す。 メタン発酵槽1に供給する有機廃棄物(発酵槽供給
液) ウルトラフィルター2透過液 減圧蒸発濃縮装置4に供給されるアンモニア固定槽3
にて無機酸添加処理した消化液 減圧蒸発濃縮装置4で処理した濃縮液(蒸発濃縮液) 粉末肥料。 また表2には、前述の通り製造した本発明粉末肥料−1
と−2の肥料成分及び肥効促進剤の含有量を示す。な
お、表1及び表2中の%は重量%である。
Table 1 shows a case where a phosphoric acid solution is used for fixing ammonia (manufacture of the powder fertilizer-1 of the present invention) and a case where sulfuric acid is used for fixation of ammonia (manufacture of the powder fertilizer-2 of the present invention). The material balance in each step indicated by the symbols 1 to 3 is shown. Organic waste supplied to the methane fermentation tank 1 (fermentation tank supply liquid) Ultrafilter 2 Permeate Liquid Ammonia fixing tank 3 supplied to reduced pressure evaporation concentration device 4
Digestive liquid treated with the addition of an inorganic acid in 1. Concentrated liquid (evaporated concentrated liquid) treated with the reduced pressure evaporative concentrator 4. Powdered fertilizer. In addition, in Table 2, the powdered fertilizer-1 of the present invention produced as described above.
Content of fertilizer component and fertilizer effect accelerator of -2 is shown. In addition,% in Table 1 and Table 2 is weight%.

【0036】[0036]

【表1】 [Table 1]

【0037】[0037]

【表2】 [Table 2]

【0038】実施例2:小松菜の栽培テスト 実施例1で得られた本発明粉末肥料−1及び本発明粉末
肥料−2の肥効促進効果を確かめるべく、これらの粉末
肥料と同等量の窒素(N)、リン酸(P25)およびカ
リ(K2O)を、本発明粉末肥料−1に対してはリン酸
アンモニウム、炭酸カリおよび硫酸カリを用い、また本
発明粉末肥料−2に対しては硫酸アンモニウム、炭酸ア
ンモニウム、リン酸アンモニウム、リン酸カリなどを用
いて調製した溶液(比較対照肥料1−および−2)と、
小松菜の栽培テストを行った。その結果を表3に示す。
なお、このテストでは、土壌として火山灰下層土を用
い、また育成の期間は平成13年5月14日播種より6
月8日までの25日間であった。
Example 2 Komatsuna Cultivation Test In order to confirm the effect of promoting the fertilization effect of the powdered fertilizer-1 of the present invention and the powdered fertilizer-2 of the present invention obtained in Example 1, nitrogen equivalent to these powdered fertilizers ( N), phosphoric acid (P 2 O 5 ) and potassium (K 2 O), ammonium phosphate, potassium carbonate and potassium sulfate were used for the powder fertilizer-1 of the present invention, and powder fertilizer-2 of the present invention was used. On the other hand, a solution prepared using ammonium sulfate, ammonium carbonate, ammonium phosphate, potassium phosphate, etc. (comparative control fertilizers 1- and -2),
The cultivation test of Komatsuna was conducted. The results are shown in Table 3.
In this test, volcanic ash subsoil was used as soil, and the growing period was 6 after seeding on May 14, 2001.
It was 25 days until the 8th of the month.

【0039】[0039]

【表3】 [Table 3]

【0040】表3の結果から、本発明に係る肥効促進剤
入り肥料は、同等量の窒素(N)、リン酸(P25)お
よびカリ(K2O)を用いて栽培した場合と比べて、小
松菜の生育を促進することが明らかとなった。
From the results shown in Table 3, the fertilizer containing the fertilizer promoting agent according to the present invention was cultivated using the same amount of nitrogen (N), phosphoric acid (P 2 O 5 ) and potassium (K 2 O). It was revealed that the growth of Komatsuna was promoted compared with.

【0041】[0041]

【発明の効果】以上説明した通り、本発明によれば、有
機廃棄物の生物処理において生じる消化液から、植物の
肥効促進効果を有する肥効促進剤入り肥料を提供するこ
とができる。この肥効促進剤入り肥料は、植物の生育を
大幅に増加することができるので、農業生産性を大幅に
高めることができる。またこの肥効促進剤は、植物及び
ヒトを含む動物に対する安全性が高い。
As described above, according to the present invention, it is possible to provide a fertilizer containing a fertilizer accelerating agent having a plant fertilizer accelerating effect from the digestive juice produced in the biological treatment of organic waste. Since this fertilizer containing a fertilizer enhancer can significantly increase the growth of plants, it can significantly increase agricultural productivity. Moreover, this fertilizer is highly safe for plants and animals including humans.

【図面の簡単な説明】[Brief description of drawings]

【図1】 本発明に係る肥効促進剤の製造方法を説明す
るために製造プロセスの概要を示す概略図である。
FIG. 1 is a schematic diagram showing an outline of a manufacturing process for explaining a method for manufacturing a fertilizer effect enhancer according to the present invention.

【符号の説明】[Explanation of symbols]

1 メタン発酵槽 2 ウルトラフィルター 3 アンモニア固定槽 4 減圧蒸発濃縮装置 5 噴霧乾燥装置 1 methane fermentation tank 2 Ultra filter 3 Ammonia fixing tank 4 Vacuum evaporation concentrator 5 Spray dryer

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D034 AA26 BA01 CA12 4H061 AA02 FF07 GG19 GG22 GG50 LL02    ─────────────────────────────────────────────────── ─── Continued front page    F-term (reference) 4D034 AA26 BA01 CA12                 4H061 AA02 FF07 GG19 GG22 GG50                       LL02

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 有機廃棄物のメタン発酵処理液をウルト
ラフィルターに通して得られるウルトラフィルター透過
消化液を、濃縮・乾燥して肥効促進剤を含む肥料を得る
ことを特徴とする肥効促進剤入り肥料の製造方法。
1. Fertilization promotion, characterized in that an ultrafilter-digested digested liquid obtained by passing a methane fermentation treatment liquid of organic waste through an ultrafilter is concentrated and dried to obtain a fertilizer containing a fertilization promoter. Method for manufacturing fertilizer containing agents.
【請求項2】 濃縮・乾燥する前の消化液に無機酸を加
え、該消化液中のアンモニアをアンモニウム塩とした
後、濃縮・乾燥することを特徴とする請求項1に記載の
肥効促進剤入り肥料の製造方法。
2. The fertilization promotion according to claim 1, wherein an inorganic acid is added to the digestive juice before concentration / drying to make ammonia in the digestive juice to be an ammonium salt and then concentrated / dried. Method for manufacturing fertilizer containing agents.
【請求項3】 消化液を濃縮・乾燥する際に、該液を減
圧蒸発濃縮装置によって濃縮液とし、次いで該濃縮液を
噴霧乾燥装置によって粉末に乾燥すること、及びこれら
の濃縮・乾燥を80℃以下の温度で行うことを特徴とす
る請求項1に記載の肥効促進剤入り肥料の製造方法。
3. When the digestive juice is concentrated and dried, the solution is made into a concentrated solution by a reduced pressure evaporation concentrator, and then the concentrated solution is dried into a powder by a spray dryer, and the concentration and drying thereof are carried out. The method for producing a fertilizer containing a fertilizer accelerating agent according to claim 1, wherein the method is performed at a temperature of ℃ or less.
【請求項4】 請求項1から3のいずれか1項に記載の
製造方法によって得られた肥効促進剤入り肥料。
4. A fertilizer containing a fertilizer, which is obtained by the method according to any one of claims 1 to 3.
【請求項5】 さらに少なくとも1種の肥料成分を混合
したことを特徴とする請求項4に記載の肥効促進剤入り
肥料。
5. The fertilizer containing a fertilizer accelerating agent according to claim 4, further comprising at least one fertilizer component.
JP2001246574A 2001-08-15 2001-08-15 Fertilizer response accelerator-containing fertilizer and method of manufacturing the same Withdrawn JP2003055077A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2001246574A JP2003055077A (en) 2001-08-15 2001-08-15 Fertilizer response accelerator-containing fertilizer and method of manufacturing the same

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
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Publication Number Publication Date
JP2003055077A true JP2003055077A (en) 2003-02-26

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Country Link
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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006212605A (en) * 2005-02-07 2006-08-17 Nippon Sharyo Seizo Kaisha Ltd Organic waste liquid treatment apparatus and method
JP2008093523A (en) * 2006-10-06 2008-04-24 Nippon Sharyo Seizo Kaisha Ltd Apparatus and method for treating organic waste liquid
JP2008207118A (en) * 2007-02-27 2008-09-11 Hiroshima Univ Method, apparatus and system for treating ammonia nitrogen-containing waste water
JP2009244089A (en) * 2008-03-31 2009-10-22 Toden Kogyo Co Ltd Removing method and removing device of radioactive material and toc
CN107683329A (en) * 2015-04-16 2018-02-09 科陆能源亚洲私人有限公司 Improved biogas production system and preparation method thereof
JP2018168274A (en) * 2017-03-29 2018-11-01 住友大阪セメント株式会社 Biogas utilization method, biogas utilization system and biogas
WO2020071687A1 (en) * 2018-10-05 2020-04-09 문성우 Circulation-type biogas producing system through control of inorganic acids

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006212605A (en) * 2005-02-07 2006-08-17 Nippon Sharyo Seizo Kaisha Ltd Organic waste liquid treatment apparatus and method
JP2008093523A (en) * 2006-10-06 2008-04-24 Nippon Sharyo Seizo Kaisha Ltd Apparatus and method for treating organic waste liquid
JP4568264B2 (en) * 2006-10-06 2010-10-27 日本車輌製造株式会社 Organic waste liquid processing apparatus and processing method
JP2008207118A (en) * 2007-02-27 2008-09-11 Hiroshima Univ Method, apparatus and system for treating ammonia nitrogen-containing waste water
JP2009244089A (en) * 2008-03-31 2009-10-22 Toden Kogyo Co Ltd Removing method and removing device of radioactive material and toc
CN107683329A (en) * 2015-04-16 2018-02-09 科陆能源亚洲私人有限公司 Improved biogas production system and preparation method thereof
JP2018168274A (en) * 2017-03-29 2018-11-01 住友大阪セメント株式会社 Biogas utilization method, biogas utilization system and biogas
WO2020071687A1 (en) * 2018-10-05 2020-04-09 문성우 Circulation-type biogas producing system through control of inorganic acids

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