JPS61242979A - Manufacture of compost utilizing general and industrial wastes - Google Patents

Manufacture of compost utilizing general and industrial wastes

Info

Publication number
JPS61242979A
JPS61242979A JP60084783A JP8478385A JPS61242979A JP S61242979 A JPS61242979 A JP S61242979A JP 60084783 A JP60084783 A JP 60084783A JP 8478385 A JP8478385 A JP 8478385A JP S61242979 A JPS61242979 A JP S61242979A
Authority
JP
Japan
Prior art keywords
soil
water
waste
compost
animal
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP60084783A
Other languages
Japanese (ja)
Inventor
有馬 忠純
上野 富吉
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.)
GENDAI KENSETSU KK
Original Assignee
GENDAI KENSETSU 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 GENDAI KENSETSU KK filed Critical GENDAI KENSETSU KK
Priority to JP60084783A priority Critical patent/JPS61242979A/en
Publication of JPS61242979A publication Critical patent/JPS61242979A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (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】 に)産業上の利用分野 この発明は有機性汚泥あるいはthfI!物性残渣、有
機性汚泥または動植物性残渣の焼却灰、及び家畜のふん
尿の三種の混合廃棄物を地面に造成された堆肥製造用ピ
ット内で堆肥化する堆肥製造法に関するものである。
[Detailed Description of the Invention] B) Industrial Application Field This invention is applicable to organic sludge or thfI! The present invention relates to a compost production method in which three types of mixed waste: physical residue, organic sludge or incineration ash of animal and plant residue, and livestock excrement are composted in a compost production pit built on the ground.

(ロ) 従来の技術 現在状が国の農地では、化学肥料を中心として使用され
ているため、土壌が酸性化して連作障害を来し、有機物
が不足のため通気性も劣り、このため有機性肥料の必要
性が強く要望されている。
(b) Conventional technology Currently, chemical fertilizers are mainly used in the country's agricultural lands, which causes the soil to become acidic and cause continuous cropping problems, and lack of organic matter, resulting in poor aeration. There is a strong need for fertilizer.

また含水量の大きい各種汚泥の堆目巴化のため水分の低
減剤として鋸屑類が使用されていたが、鋸屑類には有機
分解し難い物質を含有している。
In addition, sawdust has been used as a moisture reducing agent to turn various types of sludge with high water content into compost, but sawdust contains substances that are difficult to decompose organically.

ため、低減剤としては不適当であった。Therefore, it was unsuitable as a reducing agent.

(ハ)発明が解決しようとする問題点 土壌の酸性化を防止するため、従来の化学肥料に代えて
、有機質肥料である堆肥を大量且つ安価に製造する必要
がある。
(c) Problems to be Solved by the Invention In order to prevent acidification of soil, it is necessary to produce compost, which is an organic fertilizer, in large quantities and at low cost in place of conventional chemical fertilizers.

また各種汚泥等の水分の低減剤として使用された鋸屑類
は、リグニン、テルペン、セルローズ等の有機分解し難
い物質を含有しているため堆肥化し雌いので、これに代
えて水分の低減剤として適当な有機性廃棄物の焼却灰を
使用する必要がある。
In addition, sawdust used as a water reducing agent for various types of sludge is difficult to compost because it contains substances that are difficult to decompose, such as lignin, terpenes, and cellulose, so it can be used as a water reducing agent instead. Appropriate organic waste incineration ash should be used.

に)問題点を解決するための手段 本発明の空気供給及び集排水浄化機構を具備し地面に造
成された堆肥製造用ピット内での堆肥製造の寮施例を図
面に基づいて説明する。
B) Means for Solving the Problems An example of a dormitory equipped with the air supply, collection and drainage purification mechanism of the present invention and producing compost in a compost production pit built on the ground will be described with reference to the drawings.

第1図のように地面に湧水しない程度に深さ約1〜2m
の堆肥製造用ピットを造成し、側面擁壁1には崩壊防止
のため約60度の勾配を、底部2には集水用として約2
00分の1の水勾配を付し、その勾配下辺末端には第4
図のようにを面2より約lIn下部に集水渠8を設け、
ピット及び集水渠8内部全面を塩化ビニール系または酢
酸ビニール系の止水S’−)4でライニングして遣水工
事を行なう。
As shown in Figure 1, the depth is approximately 1 to 2 m to the extent that water does not spring to the ground.
A compost production pit was created, and the side retaining wall 1 had a slope of about 60 degrees to prevent collapse, and the bottom part 2 had a slope of about 2 degrees to collect water.
A water gradient of 1/00 is attached, and a fourth
As shown in the figure, a water collection culvert 8 is provided approximately lIn below surface 2.
The entire interior of the pit and water collection culvert 8 is lined with vinyl chloride-based or vinyl acetate-based water stopper S'-) 4 to perform water supply work.

なおこの上水シート4の代りにゴムシートを使用する場
合もある。
Note that a rubber sheet may be used instead of the clean water sheet 4.

次に集水渠8の中央部に孔径的5uの小孔を周囲に有す
る直径3001稈度の多孔管6を勾配約200分の1に
敷設し、またこの多孔管6には数個の多孔枝管5′を付
設する。
Next, a perforated pipe 6 with a diameter of 3001 culm and having small holes of 5u in diameter around it is laid in the center of the water collection culvert 8 at a slope of about 1/200, and this perforated pipe 6 has several perforated branches. A pipe 5' is attached.

多孔管5および多孔枝管52の各内部には夫々粒径約7
1程度の小砂利6を、また各外部には夫々粒径約25f
l程度の砂利、砕石類7を充填する。
Inside each of the porous pipe 5 and the porous branch pipe 52, there is a particle size of about 7
1 small gravel 6, and each outer part has a particle size of about 25 f.
Fill with approximately 1 liter of gravel and crushed stone.

更に多孔管5の末端には上部にブロワー8を備え庇部に
排水用貯留桝9を有するコンクリート製竪型給気管1G
を設け、また底部の排水用貯留桝9に貯留された排水の
水位に応じて作動するフロートスイッチ付水中モーター
12及び水中メンプ11を陀設する。
Further, at the end of the perforated pipe 5, there is a concrete vertical air supply pipe 1G having a blower 8 at the top and a drainage storage basin 9 at the eave.
A submersible motor 12 with a float switch and a submersible pump 11 are also installed, which operate according to the water level of the wastewater stored in the drainage storage basin 9 at the bottom.

図中18は排水処理装置、14は地表水がA、B、C積
層内部への流入を防止するための開渠、15は開渠用泥
溜桝、16はみだりに人が堆肥製造場所に立入ることを
防止する囲い、17は鉄111!扉である。
In the figure, 18 is a wastewater treatment equipment, 14 is an open channel to prevent surface water from flowing into the A, B, and C stacks, 15 is a mud basin for the open channel, and 16 is a place where people stand in the compost production area. The enclosure that prevents people from entering, 17 is iron 111! It's a door.

上記のように地面に造成された堆IIl!製造用ピット
の底部2のと面に保護土壌として覆土した癌層土壌Aの
上に有機性汚泥あるいは動植物性残渣、水分低減剤とし
て従来の鋸屑に代えた有晴性汚泥または動植物性残渣の
焼却灰、及び家畜のふん尿の三種の混合廃棄物Bを撒布
し、そのとに悪臭防止用、とじての通常土壌Cを覆土す
る。
A bank built on the ground as shown above! Organic sludge or animal and plant residues are placed on top of the cancer layer soil A that is covered with protective soil on the bottom surface of the bottom 2 of the production pit, and incineration of fine-air sludge or animal and plant residues is used as a moisture reducing agent in place of conventional sawdust. Mixed waste B of three types, ash and livestock excrement, is spread, and the soil is covered with regular soil C to prevent bad odors.

なお、本発明で使用される有機性汚泥、動植物性残渣及
び家畜ふん尿は次記のとおりである。
The organic sludge, animal and plant residues, and livestock manure used in the present invention are as follows.

11)  有機性汚泥 排水処理より生ずる汚泥、製紙汚泥、ビルピット汚泥(
し尿を除く)、下水処理汚泥、染色処理汚泥、染色排水
処理汚泥、クリーニング排水処理汚泥、下水道管洗滌汚
泥、イースト省培養残渣、粉末スープ類、廃液体消化剤
11) Sludge generated from organic sludge wastewater treatment, paper manufacturing sludge, building pit sludge (
(excluding human waste), sewage treatment sludge, dyeing treatment sludge, dyeing wastewater treatment sludge, cleaning wastewater treatment sludge, sewer pipe cleaning sludge, yeast culture residue, powdered soups, liquid waste extinguishers.

(2)  動物性浅漬 ハム、ソーセージ、ベーコン、スクリーン残渣、あら、
卵から、甲から、チーズかす、製品かす。
(2) Pickled animal ham, sausage, bacon, screen residue, oh...
From eggs, shells, cheese dregs, product dregs.

(8)  !物性残渣 野菜、果実、漬物かす、小麦、米、大豆醸造かす、香辛
料残渣、パン屑、生地層、澱粉、飴かす、おから、ma
造かす、コーヒーかす。
(8)! Physical property residue Vegetables, fruits, pickle residue, wheat, rice, soybean brewing residue, spice residue, bread crumbs, dough layer, starch, candy residue, okara, ma
Coffee grounds.

(4)  家畜ふん尿 鶏ふん、豚ふん、牛ふん。(4) Livestock manure Chicken dung, pig dung, cow dung.

(ホ)作用 )[A%B、CIIWII内部は、時間の経過と共に微
生物及びバクテリアの作用により、次tsに有機分解し
て温度がと昇し始める。
(E) Effect) [A%B, As time passes, the temperature inside CIIWII begins to rise due to organic decomposition due to the action of microorganisms and bacteria.

その間定期的にブロワー8を稼動してA、 B、CW1
1内部に空気を送入し、積層内部を好気性雰囲気に保持
すると、微生物及びバクテリアの活動による混合廃棄物
Bの有機的分解の結集積層内部の温度は次第に上昇して
60℃〜70℃の恒常状態となり、雑菌は死滅する。
During that time, blower 8 is operated periodically to control A, B, and CW1.
1. When air is introduced into the interior and the inside of the stack is maintained in an aerobic atmosphere, the temperature inside the stack gradually rises to 60℃ to 70℃ due to the organic decomposition of mixed waste B due to the activities of microorganisms and bacteria. A constant state is reached and the bacteria die.

この状態になるには、夏冬等の外部温度に左右されるが
、平均80日間で達し、堆肥化工程は終了する。
This state is reached in an average of 80 days, depending on the external temperature in summer and winter, and the composting process is completed.

次に堆肥化工程中の雨水は、A%B、C@@中に多少滲
透するが、大部分は表面より外部に流れ、地表水となっ
て開渠14より放流される。
Next, rainwater during the composting process percolates into A%B, C@@ to some extent, but most of it flows to the outside from the surface and is discharged from the open channel 14 as surface water.

外部に放流されない滲透水の一部は、堆肥熱によって蒸
発して発散し、発散しない残余分は自然に沈降してピッ
ト底面2の水勾配にそって下方の集水渠8に導かれ、多
孔管5及び多孔枝管5゛の各外部の砂利、砕石@7を経
て多孔管5および多孔枝管5′の内部に入り、各内部に
充填された小砂利6中を流れて砂利、砕石類7及び小砂
利6表面に付着した微生物、バクテリアによる接触酸化
により浄化されつつ竪m給気管10の下端に設けられた
排水貯留桝9に落下流入する。
A part of the permeated water that is not discharged to the outside is evaporated and dissipated by the heat of the compost, and the remainder that is not dissipated naturally settles and is guided downward to the water collection channel 8 along the water gradient of the pit bottom surface 2, and is passed through the porous pipe. 5 and the perforated branch pipe 5', enter the inside of the perforated pipe 5 and the perforated branch pipe 5' through gravel and crushed stones @ 7, and flow through the small gravel 6 filled inside each of them to form gravel and crushed stones 7. The water is purified by contact oxidation by microorganisms and bacteria attached to the surface of the small gravel 6, and then falls and flows into the wastewater storage basin 9 provided at the lower end of the vertical air supply pipe 10.

この際プロ〒−8の糠動により多孔管5および多孔枝管
5゛を経てA、B、C積層内部と集水渠8内に空気を送
入し好気性雰囲気に保持すると、上記のように混合廃棄
物Bの有機分解を促進すると共に集水渠8内の砂利、砕
石#I7及び多孔管6と多孔枝管5内部の小砂利6表面
に付着した微生物、バクテリアの活動を促進し、排水中
の有機物は分解して浄化される。
At this time, air is introduced into the A, B, C laminated interior and the water collection culvert 8 through the perforated pipe 5 and the perforated branch pipe 5 by the action of Pro-8 to maintain an aerobic atmosphere, as shown above. It promotes the organic decomposition of the mixed waste B and also promotes the activity of microorganisms and bacteria attached to the surface of the gravel and crushed stones #I7 in the water collection channel 8 and the small gravel 6 inside the porous pipe 6 and the porous branch pipe 5, and organic matter is decomposed and purified.

この浄化された排水の貯留桝9内部の水位が規定水位に
達すると、フロートスイッチ付モーター12が稼動し、
水中ポンプ11により排水は地上tこ導かれる。なお規
定水位の設定は多孔管6の中心にあるブロワー8の給気
を妨げない。
When the water level inside the purified waste water storage basin 9 reaches a specified water level, the motor 12 with a float switch starts operating.
A submersible pump 11 directs the waste water to the ground. Note that the setting of the specified water level does not interfere with the air supply to the blower 8 located at the center of the porous pipe 6.

地上に揚水された排水は、その水質が排水基準値以下の
場合はそのまま放流され、排水基準値以下の場合は排水
処理装!f18に導かれて、再処[後放流される。
If the water quality is below the wastewater standard value, the wastewater pumped to the ground will be discharged as is, and if it is below the wastewater standard value, it will be treated with a wastewater treatment system! It is guided to f18 and is reprocessed and then released.

(へ)効果 本発明による有機性汚泥あるいは動植物性残渣、有機性
汚泥または動植物性残渣のa!却灰、及び寮畜のふん尿
の三彌の混合#il/i物を空気供給及び集排水浄化機
構を具備し地面に造成された堆肥製造用ピットにおいて
大量且つ安価に堆肥化することは、従来の機構装置内の
みで堆肥化する工法とは全く異なる独創的なもので、公
害防止とにおいても大きな意義を有するものである。
(f) Effects of organic sludge or animal and plant residues according to the present invention, organic sludge or animal and plant residues a! Conventionally, it has not been possible to compost a mixture of incineration ash and dormitory animal waste in large quantities and at low cost in a compost production pit built on the ground that is equipped with an air supply, collection and drainage purification mechanism. This is an original method that is completely different from the conventional method of composting inside a mechanical device, and it is also of great significance in terms of pollution prevention.

また製造された堆肥は有機性に富み、従来の化学肥料と
異なり土壌の酸性化及び連作障害を防止し、且つ従来の
約4分の1の安価で大量製産ができるので、農家及び農
業関係者に非常に有利となったものである。
In addition, the produced compost is rich in organic matter, and unlike conventional chemical fertilizers, it prevents soil acidification and continuous cropping damage, and can be mass-produced at about one-fourth the cost of conventional fertilizers, making it a great choice for farmers and agricultural stakeholders. This was very advantageous for the people.

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

第1図は本発明堆肥製造用ピットの平面図、第2図は横
断面図、第3図は横断面図、第4図は集水渠及び竪型給
気管の部分断面並びに混合廃棄物と土壌の状態を示すも
のである。 】・・・・側面複壁、2・・・・ ピット底面、8・・
・・集水44・・・・止水シート、5・・・・多孔管、
5・・・多孔枝管、6・・・・小砂利、7・・・・砂利
、砕石類、8・・・・プロワーー9・・・・排水貯留桝
、10・・・・竪型給気管、11・・・・水中ボンデ、
12・・・・フロートスイッチ付水中モーター。 A・・・・底層土壌、B・・・・混合廃棄物、C・・・
・通常土壌。 特許出願人  現代建設株式会社 代   理   人   杉 f!   瑣 −111
t、図 #1*19*J畔
Fig. 1 is a plan view of the compost production pit of the present invention, Fig. 2 is a cross-sectional view, Fig. 3 is a cross-sectional view, and Fig. 4 is a partial cross-section of the water collection culvert and vertical air supply pipe, as well as mixed waste and soil. This indicates the state of 】・・・Side compound wall, 2... Pit bottom, 8...
... Water collection 44 ... Water stop sheet, 5 ... Porous pipe,
5...Porous branch pipe, 6...Small gravel, 7...Gravel, crushed stone, 8...Plower 9...Drainage storage basin, 10...Vertical air supply pipe , 11... underwater bonding,
12... Submersible motor with float switch. A: Bottom soil, B: Mixed waste, C...
・Normal soil. Patent applicant Gendai Kensetsu Co., Ltd. Director Sugi f!瑣 -111
t, Figure #1*19*J shore

Claims (1)

【特許請求の範囲】[Claims] 空気供給及び集排水浄化機構を具備し地面に造成された
堆肥製造用ピットの底部2の上面に保護土壌として覆土
した底層土壌Aの上に有機性汚泥あるいは動植物性残渣
、有機性汚泥または動植物性残渣の焼却灰、及び家畜の
ふん尿の三種の混合廃棄物Bを撒布し、その上に悪臭発
散防止用として通常土壌Cを覆土した後定期的にブロワ
ー8を■動して上記A、B、C積層内部に空気を送入し
、積層内部を好気性雰囲気に保持し、微生物及びバクテ
リアの活動により混合廃棄物Bを有機分解して堆肥化す
ることを特徴とする、一般及び産業廃棄物を利用した堆
肥製造法。
Organic sludge or animal and plant residues, organic sludge or animal and plant residues are placed on top of the bottom layer soil A, which is covered with soil as protective soil on the top surface of the bottom 2 of a compost production pit that is equipped with an air supply, collection and drainage purification mechanism and is created on the ground. Three types of mixed waste B, consisting of residual incineration ash and livestock excrement, are spread, and after covering the waste with regular soil C to prevent the emission of bad odors, the blower 8 is periodically operated to perform the above A, B, General and industrial waste, which is characterized by introducing air into the laminated layer C, maintaining the inside of the laminated layer in an aerobic atmosphere, and organically decomposing the mixed waste B and composting it through the activities of microorganisms and bacteria. Compost production method used.
JP60084783A 1985-04-20 1985-04-20 Manufacture of compost utilizing general and industrial wastes Pending JPS61242979A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP60084783A JPS61242979A (en) 1985-04-20 1985-04-20 Manufacture of compost utilizing general and industrial wastes

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60084783A JPS61242979A (en) 1985-04-20 1985-04-20 Manufacture of compost utilizing general and industrial wastes

Publications (1)

Publication Number Publication Date
JPS61242979A true JPS61242979A (en) 1986-10-29

Family

ID=13840293

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60084783A Pending JPS61242979A (en) 1985-04-20 1985-04-20 Manufacture of compost utilizing general and industrial wastes

Country Status (1)

Country Link
JP (1) JPS61242979A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03159981A (en) * 1989-11-17 1991-07-09 Takano:Kk Production of mature fermented compost
JP2001302379A (en) * 2000-04-17 2001-10-31 Nishimatsu Constr Co Ltd Composting device and composting method for cut tree at cutting site
JP2007029927A (en) * 2005-07-29 2007-02-08 Fujimori Kogyo Co Ltd Apparatus and facility for fermenting organic matter
CN109265208A (en) * 2018-11-15 2019-01-25 贵州省三好食品开发有限公司 Discarded bean dregs organic fertilizer and preparation method thereof

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03159981A (en) * 1989-11-17 1991-07-09 Takano:Kk Production of mature fermented compost
JP2001302379A (en) * 2000-04-17 2001-10-31 Nishimatsu Constr Co Ltd Composting device and composting method for cut tree at cutting site
JP4488456B2 (en) * 2000-04-17 2010-06-23 西松建設株式会社 Composting device and method for composting felled trees in logging site
JP2007029927A (en) * 2005-07-29 2007-02-08 Fujimori Kogyo Co Ltd Apparatus and facility for fermenting organic matter
CN109265208A (en) * 2018-11-15 2019-01-25 贵州省三好食品开发有限公司 Discarded bean dregs organic fertilizer and preparation method thereof

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