JP2652114B2 - Method for promoting fermentation of organic sludge - Google Patents
Method for promoting fermentation of organic sludgeInfo
- Publication number
- JP2652114B2 JP2652114B2 JP32491092A JP32491092A JP2652114B2 JP 2652114 B2 JP2652114 B2 JP 2652114B2 JP 32491092 A JP32491092 A JP 32491092A JP 32491092 A JP32491092 A JP 32491092A JP 2652114 B2 JP2652114 B2 JP 2652114B2
- Authority
- JP
- Japan
- Prior art keywords
- temperature
- mixture
- incinerated ash
- fermentation
- sewage sludge
- 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.)
- Expired - Fee Related
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Landscapes
- Cultivation Of Plants (AREA)
- Fertilizers (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は有機汚泥物の醗酵促進方
法に関するもので、醗酵機械や醗酵槽を一切使用しない
で、且つその醗酵機械や醗酵槽を使用したのと同じ醗酵
効果が得られ、確実に醗酵された大量の有機汚泥物がき
わめて短時間で而もきわめて安価に得られるようにした
ものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for accelerating fermentation of organic sludge, which does not use any fermentation machine or fermentation tank, and provides the same fermentation effect as using the fermentation machine or fermentation tank. A large amount of fermented organic sludge can be obtained in a very short time and very cheaply.
【0002】[0002]
【従来の技術】本願出願人は、先にPMC(ピーエムシ
ー)工法と呼ぶリサイクル緑化工法を提供した(特公平
4−45613号公報及び特開平4−261914号公
報参照)。そのPMC工法とは、公共下水汚泥や家畜糞
等の有機質の廃棄物と木炭粉、又は当該有機質の廃棄物
とパルプ製造時に生じるパルプ滓の焼却灰等各種産業か
ら発生する焼却灰を混合した後、醗酵させて有機質系の
“生育基盤材”を生産し、この生育基盤材と、コンニャ
ク飛粉を主原料とした植物性肥料「ピーエムザイ(登録
商標)」と称する粘着材を使用して、法面緑化工事にお
ける植物の生育基盤の形成を行う工法である。そして、
前記の有機質系の“生育基盤材”を生産する手段とし
て、キルン型(横型)の醗酵機を用い、一端の投入口か
ら公共下水汚泥や家畜糞等の有機質の廃棄物と焼却灰の
混合物を投入し、その醗酵機内に高温熱風を送りながら
約2日間収容して50゜C〜60゜C前後に加熱した混
合物を他端の出口から吐出させる。そして、堆積場に約
2〜3ケ月堆積しておいて醗酵を完了させる。2. Description of the Related Art The applicant of the present invention has provided a recycling greening method called PMC (PMC) method (see Japanese Patent Publication No. 4-45613 and Japanese Patent Application Laid-Open No. 4-261914). The PMC method is a method of mixing organic waste such as public sewage sludge and livestock dung and charcoal powder, or the organic waste and incinerated ash generated from various industries such as incinerated ash of pulp slag generated during pulp production. , Fermented to produce an organic "growth base material", using this growth base material and an adhesive material called "Pmzai (registered trademark)", a plant fertilizer made mainly from konjac flour, This is a method of forming a plant growth base in the greening work. And
As a means for producing the organic "growth base material", a kiln type (horizontal) fermenter is used, and a mixture of organic waste such as public sewage sludge and livestock manure and incineration ash is supplied from one input port. The mixture is charged and heated for about two days while sending high-temperature hot air into the fermenter, and the mixture heated to about 50 ° C to 60 ° C is discharged from the outlet at the other end. Then, the fermentation is completed after about 2 to 3 months of accumulation at the accumulation site.
【0003】[0003]
【発明が解決しようとする課題】上記のPMC工法によ
って、従来工法で植生基盤材として用いる黒土や山砂等
の代用となるほか、肥料分も多く含まれている。さら
に、山砂採取による自然破壊の帽子と、有機質汚泥物の
リサイクルできる現代的な工法として実施され有益であ
る。他方、前記のPMC工法において、有機質廃棄物の
醗酵促進には、水分調整の出来不出来が醗酵完了の期間
を左右する。そして、醗酵処理後、完熟するまで堆積場
に2〜3ケ月の期間堆積しておく必要がある。そのた
め、醗酵機を設置するための高額な設備投資と、醗酵機
内に高温熱風を送るための燃料費が必要となり、さらに
堆肥ととして使用できる生育基盤材が得られるまでに早
くて約2ケ月の長期間を要しているので、かなりの量を
ストックしておかないと、台風や大雨又は地滑り等によ
る法面の崩落等によって大量の生育基盤材の入用に間に
合わない恐れが往々にしてあるのが現状である。The above-mentioned PMC method substitutes black soil and mountain sand used as a vegetation base material in the conventional method, and also contains a large amount of fertilizer. In addition, it is useful and useful as a modern construction method that can recycle organic sludge and caps that destroy nature by collecting sand. On the other hand, in the above-mentioned PMC method, in the fermentation promotion of organic waste, the inability to adjust the water content determines the period of completion of fermentation. Then, after the fermentation treatment, it is necessary to accumulate in the sedimentation site for a period of two to three months until it is ripe. Therefore, expensive equipment investment for installing the fermenter, fuel costs for sending high-temperature hot air into the fermenter are required, and it takes about two months to obtain a growth base material that can be used as compost. It takes a long time, so if you do not stock a considerable amount, there is often a risk that it will not be possible to use a large amount of growth base material due to landslides such as typhoons, heavy rain or landslides is the current situation.
【0004】[0004]
【課題を解決するための手段】そこで、本発明は従来工
法の課題を解決し、且つ発明の目的を達成するために提
供するものである。すなわち本発明は有機汚泥物の醗酵
促進方法において、公共下水汚泥に木質性の焼却灰とし
て粉状のパルプ滓高温焼却灰又は間伐材若しくは建設資
材製造時に発生する屑木材を炭化した焼却灰を少なくと
も約100゜Cを維持している間にタイヤショベルカー
で50:50の配合比率で攪拌混合し、前記の公共下水
汚泥と粉状の高温焼却灰の混合物の自熱温度を40゜C
〜80゜Cを維持させ、且つ混合物の自熱温度を40゜
C〜80゜C前後に維持している間に水分調整と脱臭を
行い、その直後に通気性を有すると共に直径1m、高さ
1m、容量が約1立方米の混合物を収納できる堆積用兼
運搬用袋体に詰めて比較的短時間で自然醗酵を行うもの
である。SUMMARY OF THE INVENTION Therefore, the present invention is provided to solve the problems of the conventional method and to achieve the object of the invention. That is, the present invention relates to a method for accelerating fermentation of organic sludge, wherein at least pulp slag high temperature incineration ash or incineration ash obtained by carbonizing waste wood generated during the production of thinning materials or construction materials is used as woody incineration ash in public sewage sludge. While maintaining the temperature at about 100 ° C, the mixture was stirred and mixed at a mixing ratio of 50:50 with a tire shovel car, and the self-heating temperature of the mixture of the public sewage sludge and the powdery high-temperature incinerated ash was reduced to 40 ° C.
水分 80 ° C., while adjusting the moisture content and deodorization while maintaining the self-heating temperature of the mixture at around 40 ° C. to 80 ° C. Immediately thereafter, it has air permeability and a diameter of 1 m, height Natural fermentation is carried out in a relatively short time, packed in a bag for storage and transportation capable of storing a mixture of 1 m and a volume of about 1 cubic rice.
【0005】[0005]
【作用】焼却炉から排出された直後の粉状のパルプ滓の
焼却灰は、約300゜Cの高温の自熱を有している。そ
して、排出されていか外気に触れている前記の焼却灰は
温度が下降するが、あまり時間が経過していない状態
で、少なくとも100゜C前後を維持している間に下水
汚泥と約50:50の容量の配合比率で攪拌混合する
と、当該下水汚泥等の水分調整が行われると共に、焼却
灰が持つ性質によってかなりの脱臭が行われる。そし
て、攪拌が十分に行われた前記混合物を直ちに通気性を
有し、且つ直径1m、高さ1mで収容量が1立方米の混
合物を収納できる堆積用兼運搬用袋体に詰めて10日〜
15日間程度堆積しておくと、外気がその袋体内に適度
に浸透して醗酵の促進を助勢して完熟に至る。The incineration ash of the powdery pulp slag immediately after being discharged from the incinerator has a high temperature of about 300 ° C. The temperature of the incinerated ash that has been discharged or is in contact with the outside air decreases, but the temperature of the incinerated ash has not decreased much, and at least about 100 ° C. has been maintained. When stirring and mixing at a mixing ratio of 50 volumes, the water content of the sewage sludge and the like is adjusted, and considerable deodorization is performed due to the properties of the incinerated ash. Then, the mixture sufficiently stirred was immediately permeable to the air, packed in a stacking / transport bag capable of storing a mixture of 1 m in diameter, 1 m in height and 1 cubic rice in capacity for 10 days. ~
If it accumulates for about 15 days, the outside air permeates moderately into the bag, assists in the promotion of fermentation, and reaches full maturity.
【0006】[0006]
【実施例】次に本発明の実施例を図面を以て説明する。
図1は本発明に係る有機汚泥物の醗酵促進工程を示す概
略側面図である。図において、1は汚泥処理場で処理さ
れた公共下水汚泥であり、これが有機質廃棄物である。
2は木質性の高温焼却灰であり、具体的には製紙工場B
においてパルプ生産時に生じる粉状のパルプ滓高温焼却
灰のほか、間伐材や建設資材製造時に発生する屑木材等
を焼却して生産される炭化の焼却灰を用いるものであ
る。そして、前記パルプ滓の高温焼却灰の場合は、製紙
工場から排出されてから遠距離の醗酵物製造工場まで専
用トラック等の運搬車で搬送して到着する時間が経過し
ても100゜C前後を維持している温度を必要とする。
3は前記の専用トラック1台分の下水汚泥1と、パルプ
滓をはじめとする木質性の高温焼却灰2とを50:50
の配合比率でタイヤショベルカーCによって攪拌した混
合物であり、この混合状態において40゜C〜80゜C
の自熱を有している。4は混合物3を詰めて収容する通
気性を有する袋体であり、その収納できる容積は、混合
物内部への外気を浸透できる程度の容量とするために一
袋当たり1m3に設定し、且つ横断面の直径を1m、高
さ1m程度に設定する。Next, an embodiment of the present invention will be described with reference to the drawings.
FIG. 1 is a schematic side view showing the step of accelerating the fermentation of organic sludge according to the present invention. In the figure, reference numeral 1 denotes a public sewage sludge treated in a sludge treatment plant, which is an organic waste.
2 is a woody high-temperature incinerated ash, specifically, a paper mill B
In addition to the high-temperature incinerated pulp slag generated during pulp production, carbonized incinerated ash produced by burning thinned wood and scrap wood generated during the production of construction materials is used. In the case of the high-temperature incinerated ash of the pulp slag, even after the time of being discharged from the paper mill and transporting it to a fermented product manufacturing plant at a long distance by a truck such as a dedicated truck and arriving, the temperature is around 100 ° C. Need to maintain the temperature.
Reference numeral 3 denotes a 50:50 mixture of the sewage sludge 1 for one dedicated truck and the woody high temperature incinerated ash 2 including pulp slag.
The mixture was stirred by a tire excavator C at a mixing ratio of 40 ° C. to 80 ° C. in this mixed state.
Have self-heating. 4 is a bag body having air permeability to accommodate stuffed with mixture 3, the housing can be volume was set at 1 m 3 per bag to a capacity enough to penetrate the outside air into the mixture inside, and transverse The diameter of the surface is set to about 1 m and the height to about 1 m.
【0007】[0007]
【具体的な工程例1】製紙工場における、焼却炉から排
出された直後の粉状のパルプ滓高温焼却灰2は、約30
0゜C程度の高温の自熱を有している。そして、排出さ
れて外気に触れている前記焼却灰の温度は下降するが、
遠距離の醗酵物製造工場まで運搬車で搬送到着する時間
が経過しても少なくとも100゜C前後の自熱を維持し
ている。この焼却灰2を下水処理から専用トラックで運
搬した1台分の公共下水汚泥1と50:50の配合比率
でタイヤショベルカーCを使いそのバケットですくって
でなんども万遍なく切り返して均一に攪拌して混合す
る。これによって、高温焼却灰は一種の熱交換作用でさ
らに温度が下がるが、攪拌された混合物3は少なくとも
40゜C〜80゜C程度は維持され、その混合物に含ま
れている水分の調整が行われると共に、大量の公共下水
汚泥の強烈な悪臭ないし異臭の臭気は粉状のパルプ滓高
温焼却灰が持つ性質によってかなりの脱臭が行われる。
そして、攪拌が十分に行われた混合物3を直ちに通気性
を有する袋体4に詰めて10日〜15日間程度すの子5
を介して複数段に堆積し、且つ必要に応じてテント6で
覆っておく。外気がその袋体周囲から袋体内に適度に浸
透して醗酵の促進を助勢する。この場合、袋体の開口部
41を中身がこぼれない程度に開いておくことにより醗
酵促進が一層向上する。[Specific process example 1] In a paper mill, powdery pulp slag high temperature incineration ash 2 immediately after being discharged from an incinerator is about 30%.
It has a high temperature of about 0 ° C. Then, although the temperature of the incinerated ash discharged and touching the outside air decreases,
It maintains its own heat of at least around 100 ° C even after the arriving time at the distant fermented product manufacturing plant by transport vehicle has passed. This incinerated ash 2 was transported from the sewage treatment by a dedicated truck to one public sewage sludge 1 and the bucket was used with a tire shovel car C in a mixing ratio of 50:50 using a tire shovel car C, and it was turned back and forth uniformly. Stir and mix. As a result, the temperature of the high-temperature incinerated ash is further lowered by a kind of heat exchange action, but the temperature of the stirred mixture 3 is maintained at least about 40 ° C to 80 ° C, and the moisture contained in the mixture is adjusted. In addition, the intense foul or off-flavor odor of large amounts of public sewage sludge is considerably deodorized due to the properties of the powdered pulp slag high-temperature incineration ash.
Then, the mixture 3 having been sufficiently stirred is immediately packed in a bag 4 having air permeability, and the mixture is slivered for about 10 to 15 days.
And is covered with a tent 6 if necessary. The outside air permeates the bag from the periphery of the bag to an appropriate extent to promote fermentation. In this case, the fermentation promoting is further improved by keeping open the opening 4 1 of the bag so as not to spill.
【0009】[0009]
【具体的な工程例2】焼却灰を木質性の高温焼却灰や間
伐材又は建設資材の製造時に発生する屑木材等で得る場
合は、これらを燃焼する焼却炉に投入して燃焼して大量
の炭化焼却灰を生産し、温度が下がらないうちに、前記
工程1のパルプ滓の高温焼却灰と同じ容量で行う。[Specific process example 2] When incinerated ash is to be obtained from woody high-temperature incinerated ash or scrap wood generated during the production of thinned wood or construction materials, these are put into an incinerator that burns them and burned in large quantities. Ash is produced at the same volume as that of the high-temperature incinerated ash of the pulp slag in step 1 before the temperature is lowered.
【0010】[0010]
【発明の効果】本発明は上記の構成であるから、公共下
水汚泥に焼却炉から排出された粉状の高温焼却灰又は木
質性の高温焼却灰や間伐材又は建設資材の製造時に発生
する屑木材の焼却灰を少なくとも100゜C前後の自熱
を維持している間に50:50の配合比率で攪拌し、約
40゜C〜80゜Cの自熱を維持した状態で公共下水汚
泥の水分調整が行われると共に、高温焼却灰が持つ性質
のよって同じく前記下水汚泥の脱臭が行われる。前記の
高温焼却灰のうち、間伐材又は建設資材の製造時に発生
する屑木材を用いることは、発生しても使い途がないも
のを大量使用の途を開き、用途の拡大により特に地場産
業の活性化にも貢献する効果がある。そして、下水汚泥
と粉状のパルプ滓高温焼却灰や木質性の高温焼却灰や間
伐材又は建設資材の製造時に発生する屑木材を炭化した
高温焼却灰の混合物を直ちに通気性のある大容量の収容
ができる袋体に収納することができ、且つ混合物を詰め
た袋体を複数段に堆積しておくことにより、外気が堆積
した袋体内に適度に浸透し、自然醗酵を促進してやがて
その醗酵が完了する。そして、自然醗酵が完了した醗酵
物は袋体ごと出荷できるので、作業の省略化が図れる。
従って、本発明によれば、公共下水汚泥の醗酵させるの
に、醗酵機や醗酵槽を一切使用せず、また醗酵時に必要
なエアーレイション(混合物の攪拌混合した切り返しに
よる酸素の供給)作業も必要としないでも自然醗酵が促
進され、しかも堆積保管及び輸送に手頃な1立方米程度
の容量の通気性を有する袋体に詰めるだけで10日〜1
5日間程度堆積しておくだけの短期間で大量で且つ完全
の法面緑化工事に必要な生育基盤に適する有機汚泥の醗
酵物が得られる。According to the present invention having the above-described structure, the powdery high-temperature incinerated ash or woody high-temperature incinerated ash discharged from the incinerator into public sewage sludge, and the waste generated during the production of thinned wood or construction materials The wood incineration ash is stirred at a mixing ratio of 50:50 while maintaining the self-heat of at least about 100 ° C, and the public sewage sludge is stirred while the self-heat of about 40 ° C to 80 ° C is maintained. The moisture is adjusted, and the sewage sludge is also deodorized due to the properties of the high-temperature incinerated ash. Of the above-mentioned high-temperature incinerated ash, the use of scrap wood generated during the production of thinned wood or construction materials opens up the way of mass use of those that have no use even if they are generated, and the expansion of applications has particularly stimulated the local industry. It also has the effect of contributing to the development. Then, a mixture of sewage sludge and powdered pulp slag high-temperature incineration ash, woody high-temperature incineration ash, or high-temperature incineration ash obtained by carbonizing waste wood generated during the production of thinned wood or construction materials is immediately permeable to a large-volume gas. By accumulating a bag filled with the mixture in a plurality of stages, which can be stored in a bag that can be accommodated, the outside air permeates moderately into the bag in which the air is accumulated, and natural fermentation is promoted and eventually. Fermentation is completed. The fermented product after the natural fermentation can be shipped together with the bag, so that the operation can be omitted.
Therefore, according to the present invention, fermentation of public sewage sludge does not require any fermenter or fermentation tank, and also requires an aeration (supply of oxygen by stirring and mixing the mixture back and forth) during fermentation. Natural fermentation is promoted even if it is not necessary, and it is only 10 days to 1
It is possible to obtain a large amount of fermented organic sludge suitable for a growth base required for complete slope revegetation in a short period of time in which it is accumulated for about 5 days.
【図1】 本発明に係る有機汚泥物の醗酵促進工程を示
す概略図である。FIG. 1 is a schematic view showing a step of accelerating fermentation of organic sludge according to the present invention.
1 公共下水汚泥 2 パルプ滓等の粉状の高温焼却灰 3 40゜C〜80゜Cの混合物 4 通気性を有する袋体 5 すの子 6 テント C タイヤショベルカー DESCRIPTION OF SYMBOLS 1 Public sewage sludge 2 Powdery high-temperature incineration ash, such as pulp slag 3 Mixture of 40 degreeC-80 degreeC 4 Bag with air permeability 5 Sunoko 6 Tent C Tire excavator
Claims (1)
状のパルプ滓高温焼却灰又は間伐材若しくは建設資材製
造時に発生する屑木材を炭化した焼却灰を少なくとも約
100゜Cを維持している間にタイヤショベルカーで5
0:50の配合比率で攪拌混合し、前記の公共下水汚泥
と粉状の高温焼却灰の混合物の自熱温度を40゜C〜8
0゜Cを維持させ、且つ混合物の自熱温度を40゜C〜
80゜C前後に維持している間に水分調整と脱臭を行
い、その直後に通気性を有すると共に直径1m、高さ1
m、容量が約1立方米の混合物を収納できる堆積用兼運
搬用袋体に詰めて比較的短時間で自然醗酵を行うことを
特徴とする有機汚泥物の醗酵促進方法。Claims: 1. Maintaining at least about 100 ° C. of pulp slag high temperature incinerated ash or incinerated ash obtained by carbonizing waste wood generated during the production of thinned wood or construction material as woody incinerated ash in public sewage sludge. 5 with a tire excavator while
The mixture was stirred and mixed at a mixing ratio of 0:50, and the self-heating temperature of the mixture of the public sewage sludge and the powdery high-temperature incinerated ash was set to 40 ° C to 8 ° C.
0 ° C. and the mixture is heated to 40 ° C.
While maintaining the temperature at around 80 ° C, moisture adjustment and deodorization were carried out. Immediately thereafter, it had air permeability and was 1 m in diameter and 1 m in height.
m. A method for accelerating fermentation of organic sludge, wherein natural fermentation is carried out in a relatively short time after being packed in a bag for accumulation and transportation capable of storing a mixture of about 1 cubic rice.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
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JP32491092A JP2652114B2 (en) | 1992-11-10 | 1992-11-10 | Method for promoting fermentation of organic sludge |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
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JP32491092A JP2652114B2 (en) | 1992-11-10 | 1992-11-10 | Method for promoting fermentation of organic sludge |
Publications (2)
Publication Number | Publication Date |
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JPH07172966A JPH07172966A (en) | 1995-07-11 |
JP2652114B2 true JP2652114B2 (en) | 1997-09-10 |
Family
ID=18170990
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Application Number | Title | Priority Date | Filing Date |
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JP32491092A Expired - Fee Related JP2652114B2 (en) | 1992-11-10 | 1992-11-10 | Method for promoting fermentation of organic sludge |
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JP (1) | JP2652114B2 (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
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JP2020078790A (en) * | 2018-11-14 | 2020-05-28 | 株式会社テクノ中部 | Detoxification method for incineration ash, and incineration ash regenerated fertilizer |
Family Cites Families (6)
Publication number | Priority date | Publication date | Assignee | Title |
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JPS5317170A (en) * | 1976-08-02 | 1978-02-16 | Kawasaki Kiko Kk | Method of accelerating decompostive ripening of hull compost material |
JPS54105069A (en) * | 1978-01-25 | 1979-08-17 | Hidakamachi Yuuki Hiriyou Seis | Production of fermented excretion fertilizer |
JPS61174187A (en) * | 1985-01-24 | 1986-08-05 | 田中 功 | Compost manufacture and apparatus therefor |
JPS6434215A (en) * | 1987-07-30 | 1989-02-03 | Masaki Kawakita | Bed soil for raising seedling |
JPH02296785A (en) * | 1989-05-10 | 1990-12-07 | Koshi Yamashita | Production of fertilizer from paper mill sludge |
JPH0678630B2 (en) * | 1990-12-26 | 1994-10-05 | 上毛緑産工業株式会社 | Recycling greening base formation method |
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1992
- 1992-11-10 JP JP32491092A patent/JP2652114B2/en not_active Expired - Fee Related
Also Published As
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JPH07172966A (en) | 1995-07-11 |
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