JPH0678630B2 - Recycling greening base formation method - Google Patents
Recycling greening base formation methodInfo
- Publication number
- JPH0678630B2 JPH0678630B2 JP41496590A JP41496590A JPH0678630B2 JP H0678630 B2 JPH0678630 B2 JP H0678630B2 JP 41496590 A JP41496590 A JP 41496590A JP 41496590 A JP41496590 A JP 41496590A JP H0678630 B2 JPH0678630 B2 JP H0678630B2
- Authority
- JP
- Japan
- Prior art keywords
- compost
- base material
- pulp
- mixing
- spraying
- 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
- 238000000034 method Methods 0.000 title claims description 12
- 238000004064 recycling Methods 0.000 title description 4
- 230000015572 biosynthetic process Effects 0.000 title 1
- 239000000463 material Substances 0.000 claims description 30
- 238000005507 spraying Methods 0.000 claims description 20
- 239000002361 compost Substances 0.000 claims description 19
- 239000002893 slag Substances 0.000 claims description 19
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 17
- 239000000843 powder Substances 0.000 claims description 12
- 239000002440 industrial waste Substances 0.000 claims description 11
- 229920002752 Konjac Polymers 0.000 claims description 10
- 235000010485 konjac Nutrition 0.000 claims description 10
- 238000002156 mixing Methods 0.000 claims description 10
- 239000010791 domestic waste Substances 0.000 claims description 9
- 239000010801 sewage sludge Substances 0.000 claims description 9
- 239000000203 mixture Substances 0.000 claims description 3
- 238000000746 purification Methods 0.000 claims description 3
- 239000010802 sludge Substances 0.000 description 13
- 230000000694 effects Effects 0.000 description 10
- 238000000855 fermentation Methods 0.000 description 8
- 230000004151 fermentation Effects 0.000 description 8
- 239000002689 soil Substances 0.000 description 8
- 229910001385 heavy metal Inorganic materials 0.000 description 7
- 229920001131 Pulp (paper) Polymers 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 239000002023 wood Substances 0.000 description 5
- 238000010276 construction Methods 0.000 description 4
- 238000010586 diagram Methods 0.000 description 4
- 239000003337 fertilizer Substances 0.000 description 4
- 239000004570 mortar (masonry) Substances 0.000 description 4
- 230000008569 process Effects 0.000 description 4
- 239000002699 waste material Substances 0.000 description 4
- 230000032683 aging Effects 0.000 description 3
- 238000004061 bleaching Methods 0.000 description 3
- 230000006378 damage Effects 0.000 description 3
- 230000001877 deodorizing effect Effects 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 3
- 239000000835 fiber Substances 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 239000004576 sand Substances 0.000 description 3
- 239000007921 spray Substances 0.000 description 3
- 238000003860 storage Methods 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- 230000009471 action Effects 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 230000036541 health Effects 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 238000002347 injection Methods 0.000 description 2
- 239000007924 injection Substances 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 239000010815 organic waste Substances 0.000 description 2
- 239000003415 peat Substances 0.000 description 2
- 230000035699 permeability Effects 0.000 description 2
- 230000003405 preventing effect Effects 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 241000251468 Actinopterygii Species 0.000 description 1
- 229920002488 Hemicellulose Polymers 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 239000000853 adhesive Substances 0.000 description 1
- 230000001070 adhesive effect Effects 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 239000002585 base Substances 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 238000009264 composting Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000010411 cooking Methods 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 238000010169 landfilling Methods 0.000 description 1
- 229920005610 lignin Polymers 0.000 description 1
- 239000010871 livestock manure Substances 0.000 description 1
- 235000013372 meat Nutrition 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 230000003472 neutralizing effect Effects 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 235000010987 pectin Nutrition 0.000 description 1
- 229920001277 pectin Polymers 0.000 description 1
- 239000001814 pectin Substances 0.000 description 1
- 238000003825 pressing Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000005086 pumping Methods 0.000 description 1
- 239000011435 rock Substances 0.000 description 1
- 235000014102 seafood Nutrition 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000003516 soil conditioner Substances 0.000 description 1
- 230000000087 stabilizing effect Effects 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 235000013311 vegetables Nutrition 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Landscapes
- Pit Excavations, Shoring, Fill Or Stabilisation Of Slopes (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、人工的に造成された裸
地や、災害で崩壊した山腹又は無機質で劣性土壌の岩盤
等の法面又はゴルフ場における目土、基盤、公園緑化等
に植物を導入して緑化保護する、いわゆる法面緑化工事
に先立って施工する植生基盤を形成するのに、産業廃棄
物や生活廃棄物若しくは公共下水汚泥に、紙を製造する
ときに発生するパルプ滓(ペ−パ−スラッジ)の焼却灰
を高温の状態で加えることるにって法面緑化工事におけ
る植生用の基盤材にリサイクルして活用しようとするも
のである。[Field of Industrial Application] The present invention is applied to artificially constructed bare land, slopes such as hillsides destroyed by disasters or rocks of inorganic recessive soil, or soils, bases, park greening at golf courses, etc. In order to form a vegetation base to be installed prior to the so-called slope greening work, where plants are introduced to protect the trees from being planted, industrial waste, domestic waste or public sewage sludge is produced with pulp dregs that are produced when paper is produced. By adding incinerated ash of (paper sludge) at a high temperature, it is intended to be recycled and used as a base material for vegetation in slope greening work.
【0002】[0002]
【従来の技術】現在、地方自治体が抱えている共通の問
題の一つとして、毎日のように大量に発生する産業廃棄
物や生活廃棄物の処理がある。2. Description of the Related Art At present, one of the common problems faced by local governments is the processing of industrial and household wastes, which are generated in large quantities on a daily basis.
【0003】その中でも特に、公共下水から発生する汚
泥は年々増加し、その処理としては、燃焼、埋め立て、
海洋投棄などによって行われているが、多額の費用が掛
かると共に、環境破壊や二次公害の恐れもあって深刻な
社会問題となっている。Above all, the sludge generated from public sewage is increasing year by year, and the treatment includes burning, landfilling,
Although it is carried out by dumping in the ocean, it is a serious social problem because it costs a lot of money and there is a fear of environmental destruction and secondary pollution.
【0004】そこで、本出願人は先に、特願昭63−2
24131号において、コ−ティング肥料又は堆肥及び
コンニャクの飛粉に、燃える廃棄物の焼却灰を加えて攪
拌混合し、モルタル吹付機を用いてノズル噴射時に水を
加えて地山に所定厚さになるように吹付けて基盤層を形
成したリサイクルによる緑化基盤形成工法を提供した。Therefore, the present applicant has previously filed Japanese Patent Application No. 63-2.
No. 24131, incinerator ash of burning waste is added to coating fertilizer or compost and konjak flying powder, and the mixture is stirred and mixed, and water is added at the time of nozzle injection using a mortar spraying machine to a predetermined thickness in the ground. We provided a greening foundation forming method by recycling by spraying to form a foundation layer.
【0005】これによって、法面緑化工事において、植
生基盤材を得る手法として従来行われていた、環境破壊
につながる山地の表土や山砂、または品薄とコスト高の
外国産のピ−トモス類を使用する必要がなくなり、而も
従来の基盤材と同様に恒久的な緑化が得られた。[0005] As a result, in the slope greening work, the top soil and mountain sand of the mountainous area leading to environmental damage, which has been conventionally used as a method for obtaining the vegetation base material, or the foreign-made peet moss which are thin and expensive are used. There is no need to use it, and permanent greening was obtained just like conventional base materials.
【0006】[0006]
【発明が解決しようとする課題】ところで、本出願人が
提供した上記発明において、植生基盤材用の汚泥コンポ
ストとなる産業廃棄物や公共下水汚泥中には、非健康物
質や重金属類が含有している。現在、埋め立て場所に廃
棄しようとする「金属等を含む産業廃棄物」に係わる判
定基準(総理府令)は次のとおりである。By the way, in the above invention provided by the present applicant, non-health substances and heavy metals are contained in industrial waste and public sewage sludge, which are sludge compost for vegetation base materials. ing. Currently, the criteria (Prime Minister's Ordinance) regarding "industrial waste including metals" to be discarded at the landfill site are as follows.
【0007】[0007]
【表1】[Table 1]
【0008】他方、本願出願人が提供した前記発明にお
いて、生育基盤材として利用する汚泥焼却灰中に含まれ
る重金属等の溶出試験結果及び含有量は次のとおりであ
る。On the other hand, in the above invention provided by the applicant of the present invention, the results of elution test and the content of heavy metals contained in sludge incineration ash used as a growth base material are as follows.
【0009】[0009]
【表2】[Table 2]
【0010】[0010]
【表3】[Table 3]
【0011】従って、重金属類を含有する焼却灰を利用
した植生基盤材を法面に吹付けて植生基盤層を形成した
後に、台風や豪雨または地震等よる自然災害の発生で植
生基盤層が崩壊流失し、これが水源地または田畑もしく
は養殖池などに流れ込んでそれらを汚染する恐れがある
ものと考えられる。Therefore, after the vegetation base material using the incineration ash containing heavy metals is sprayed on the slope to form the vegetation base layer, the vegetation base layer collapses due to the occurrence of a natural disaster such as a typhoon, a heavy rain or an earthquake. It is considered that there is a risk of being washed away and flowing into water sources or fields or farm ponds and contaminating them.
【0012】[0012]
【課題を解決するための手段】そこで本発明は、従来の
リサイクルによる法面緑化工事において、生育基盤材を
吹付けて植生基盤層を形成したときに、重金属のような
有害物質が外部に溶出しないにようにすると共に、植生
基盤材として保水性、通気性、土質改良効果を利用した
最適な状態で施工できるようにしたことを目的とする。Therefore, according to the present invention, harmful substances such as heavy metals are eluted outside when a vegetation base layer is formed by spraying a growth base material in a conventional slope revegetation work by recycling. The purpose of this is not only to do so, but also to make it possible to carry out construction in an optimal state using water retention, air permeability, and soil improvement effects as vegetation base material.
【0013】本発明は上記の目的を達成するためにリサ
イクル緑化基盤形成工法において、有機質の下水汚泥又
は生活廃棄物若しくは産業廃棄物に、焼却炉から取出し
て間もない高温のパルプ滓の焼却灰を加えて60℃前後に
保持した後、醗酵・熟成して粒状又は粉末化した堆肥を
生産し、この堆肥にコンニャクの精製時に生じる飛び粉
を混合して基盤材を作製し、その基盤材を吹付機に投入
し、コンプレッサの圧縮空気によるノズル噴射時に水を
加えて混合しながら、地表面に所定の厚さの基盤層にな
るように吹付けるようにしたものである。In order to achieve the above object, the present invention is a method for forming a recycle greening base, in which organic sewage sludge or domestic waste or industrial waste is incinerated ash of high temperature pulp slag just taken out from an incinerator. After adding and holding at around 60 ℃, fermented and matured to produce granular or powdered compost, and mixing the compost with flying powder produced during the purification of konjak to make the base material, It is put into a spraying machine, and when water is added and mixed at the time of nozzle injection by compressed air of a compressor, it is sprayed so that a base layer having a predetermined thickness is formed on the ground surface.
【0014】[0014]
【実施例】以下、本発明に係るリサイクル緑化基盤形成
工法の実施例を示す。図1は基盤材の生産プラント図、
図2は本発明工法におけるパルプ滓の焼却灰を得る処理
工程を示す系統図である。EXAMPLES Examples of the method for forming a recycle greening base according to the present invention will be shown below. Figure 1 is a base material production plant diagram,
FIG. 2 is a system diagram showing a treatment process for obtaining incinerated ash of pulp slag in the method of the present invention.
【0015】前記の図1において、地表面1に吹付けて
形成した植生基盤層2の基盤材3は、堆肥4とコンニャ
クの飛粉5を混ぜて製造する。そして、前記の堆肥は、
下水汚泥又は生活廃棄物若しくは産業廃棄物等の有機質
の廃棄物6に高温のパルプ滓の焼却灰7を加え、醗酵・
熟成して粒状又は粉末化して生産する。また、前記のパ
ルプ滓の焼却灰7は、製紙工場において紙を製造すると
きに発生し、通常では排泄処理するリグニン・ヘミセル
ロ−ス・ペクチン等のパルプ滓をキルン型焼却炉で焼却
処理して製造するものであり、このパルプ滓の焼却灰
は、含水量がきわめて少なく、水分調整材として有効に
機能する。この焼却炉から取出して間もない高温の焼却
灰を用いるものである。In FIG. 1, the base material 3 of the vegetation base layer 2 formed by spraying on the ground surface 1 is manufactured by mixing the compost 4 and the konjak flying powder 5. And the compost is
Sewage sludge or organic waste 6 such as household waste or industrial waste 6 was added with incinerator ash 7 of high-temperature pulp slag to ferment it.
It is produced by aging and granulating or powdering. In addition, the above-mentioned pulp ash incineration ash 7 is generated when paper is manufactured in a paper mill, and is usually excreted, and pulp slag such as lignin, hemicellulose, and pectin is incinerated in a kiln-type incinerator. The incineration ash of this pulp slag, which is produced, has an extremely low water content and effectively functions as a moisture conditioner. The high temperature incineration ash that has just been taken out from this incinerator is used.
【0016】図2において、パルプ滓7の焼却灰ができ
るまでの工程概略を示すと、化学パルプ工程と、機械パ
ルプ工程とに分けられる。まず、化学パルプ工程におい
ては、国内や国外から得た木材チップ20を貯溜槽21に一
時貯溜し、次いで木釜22に入れ、釜内で木材チップを薬
品と蒸気で圧力をかけながらどろどろに溶かしてパルプ
化し、洗浄機23で洗って繊維だけを取出し、スクリ−ン
24でゴミを取除き、さらに漂白機25にかけた後、再度ス
クリ−ン26を通して抄紙機27にかけて上質紙用パルプが
できる。一方、機械パルプ工程にあっては、丸太27を貯
木場28に運び、これをドラムバ−カ−29にかけて樹皮を
取除き、次いで砕木機30ですり潰して繊維をばらばらに
し、さらにスクリ−ン31を通して漂白機32でにかけた
後、再度スクリ−ン33に通して抄紙機34にかけて新聞紙
用パルプができる。前記の抄紙機27、34から滓となって
出た木質系繊維は、クラリファイヤ−35を通り、次いで
脱水機36に送り、最後にキルン型焼却炉37でパルプ滓を
燃焼してその焼却灰が排出される。In FIG. 2, the outline of the steps until the incineration ash of the pulp slag 7 is formed is divided into a chemical pulp step and a mechanical pulp step. First, in the chemical pulp process, wood chips 20 obtained from domestic or foreign countries are temporarily stored in a storage tank 21, and then put into a wooden kettle 22, and the wood chips are melted in a thick manner while applying pressure with chemicals and steam in the kettle. To pulp, wash with a washer 23, remove only the fibers, and
After removing the dust at 24 and further applying it to the bleaching machine 25, it is passed through the screen 26 again to the paper making machine 27 to produce fine paper pulp. On the other hand, in the mechanical pulp process, the log 27 is conveyed to the storage area 28, the bark is removed by applying it to the drum barker 29, and then the wood is crushed with a wood grinder 30 to separate the fibers, and further passed through a screen 31. After bleaching with the bleaching machine 32, it is again passed through the screen 33 and then with the paper machine 34 to produce pulp for newsprint. The wood-based fibers discharged from the paper machines 27 and 34 as slag pass through the clarifier-35 and then to the dehydrator 36, and finally burn the pulp slag in the kiln type incinerator 37 to incinerate the ash. Is discharged.
【0017】次に、前記堆肥4の具体的製造工程は次の
とおりである。例えば有機質の公共下水汚泥6を醗酵槽
を備えている醗酵機8に投入し、これと一緒に前記の焼
却炉から取出して間もない 100℃以上ある高温のパルプ
滓の焼却灰7を投入すると、前記の汚泥と混合され、そ
の汚泥の低温により、熱交換作用で温度が下がるが、少
なくとも60℃前後を保って完全熟成させることにより、
比較的さらさらした砂粒状の堆肥4が得られる。そし
て、この堆肥は、有機質であって、肥料成分(N.P.
Kその他のミネラル) を含有し、また酸性土壌の中和す
る機能もあり、土壌改良効果を発揮する。前記の高温の
パルプ滓焼却灰7を汚泥等と混合することは、醗酵熱と
して利用でき、醗酵の促進が図れることと、併せて従来
方法では、醗酵熱を保持するためにバ−ナ−を使用して
いたが、温度調整としてバ−ナ−を必要としない。さら
に、パルプ滓の焼却灰7は、有機炭素が10%から15%程
度含まれていて、脱臭作用又は重金属等非健康物質の吸
着による流失防止作用を成している。Next, the concrete manufacturing process of the compost 4 is as follows. For example, if the organic public sewage sludge 6 is put into a fermenter 8 equipped with a fermenter, and along with this, the incinerator ash 7 of a high temperature pulp slag at 100 ° C or higher, which has just been taken out from the incinerator, is put in. , Mixed with the above sludge, the temperature of the sludge is lowered by heat exchange action due to the low temperature of the sludge, but by completely aging at least around 60 ° C,
A relatively free-flowing sand-grained compost 4 is obtained. And, this compost is organic, and the fertilizer component (NP.
K and other minerals), it also has the function of neutralizing acidic soil and exerts a soil improvement effect. Mixing the high-temperature pulp slag incineration ash 7 with sludge or the like can be used as fermentation heat, and can promote fermentation, and in the conventional method, a burner can be used to retain the fermentation heat. Although it was used, it does not require a burner for temperature control. Further, the incinerated ash 7 of pulp slag contains about 10% to 15% of organic carbon, and has a deodorizing action or a washout preventing action due to adsorption of non-health substances such as heavy metals.
【0018】次に、下水汚泥は、公共の下水道から生じ
るヘドロその他の生の泥土物を主とし、また生活廃棄物
は、家庭から出る野菜・魚の調理屑、その他の生ゴミ
類、さらに産業廃棄物は、業務用に扱う大量の魚介類、
畜肉類の加工残滓等がある。に処理されたものが適当で
ある。図中、9は堆肥4に、コンニャクの飛粉5を加え
て攪拌する混合機、10は前記混合機9によって得た吹付
基盤材3を吹付けるためのモルタル吹付機、11は吹付基
盤材3を吹付ホ−ス12の先端ノズル部13に圧送するため
のコンプレッサ、14はノズル部において、水ホ−ス12′
を通じて貯水タンク15に水を加えるための動力噴霧機、
16は吹付機10へのベルトコンベヤ用及び動力噴霧機17の
駆動用発電機、18は水源19から汲水する揚水ポンプであ
る。前記のコンニャクの飛粉は、植物性の粘着材であっ
て、吹付材料の安定効果があると共に、肥料効果も兼ね
備えたものである。Next, sewage sludge is mainly sludge and other raw mud produced from public sewers, and domestic waste is cooking scraps of vegetables and fish from households, other raw garbage, and industrial waste. The thing is a large amount of seafood handled for business,
There are processing residues of meat and the like. Those processed to are suitable. In the figure, 9 is a mixer for adding konjak flying powder 5 to compost 4 and stirring, 10 is a mortar spraying machine for spraying the sprayed base material 3 obtained by the mixer 9, 11 is a sprayed base material 3 Of the spray hose 12 to the tip nozzle part 13 of the spray hose 12, and 14 is a water hose 12 'at the nozzle part.
Power sprayer for adding water to the water tank 15 through,
Reference numeral 16 is a generator for the belt conveyor to the spraying machine 10 and for driving the power sprayer 17, and 18 is a pump for pumping water from a water source 19. The above-mentioned konjak flying powder is a plant-based adhesive material, and has both a stabilizing effect on the spraying material and a fertilizer effect.
【0019】本発明の施工にあたり、堆肥をベルトコン
ベヤ又はショベル等によって混合機9に投入し、さら
に、コンニャクの飛粉5を投入して混合機内で攪拌す
る。法面の吹付け面積=100 平方m、吹付け厚さt=10
cmにおける配合は、次のとおりである。 (使用材料) (数 量) ○ 堆肥(パルプ滓焼却灰と有機質汚泥 の混合醗酵・熟成物) 15,300.0 l ○ コンニャクの飛粉(ピ−エムザイ=登録商標)255.0 kgIn the construction of the present invention, the compost is charged into the mixer 9 by a belt conveyor, a shovel or the like, and further, the konjak flying powder 5 is charged and stirred in the mixer. Spraying area of slope = 100 square meters, spraying thickness t = 10
The composition in cm is as follows. (Materials used) (quantity) ○ Compost (pulp slag incineration ash and organic sludge mixed fermentation and aged product) 15,300 0.0 l ○ Konjak flying powder (Pemzai = registered trademark) 255.0 kg
【0020】上記の配合割合によって得た吹付基盤材を
ベルトコンベヤでモルタル吹付機10に投入し、コンプレ
ッサ11の圧搾空気によってノズル部13に圧送し、同時に
水源9 から水を別の水ホ−ス12′を通じて前記ノズル部
に送り、吹付基盤材3と一緒に地山1に吹付けて植生基
盤層2を形成する。前記の植生基盤層2は、用途に応じ
て、その植生基盤層の表面に緑化ネットを張設したもの
(特公昭62−21937号「特許第1416457
号」)や、排水処理工法(特公昭62−1050号「特
許第1396451号)、(特公平1−4012号「特
許第1522804号」)及び丸太伏せ工法(特開昭6
2−182316号) のそれぞれの施工に適用すること
ができる。The sprayed base material obtained by the above mixing ratio is put into the mortar spraying machine 10 by the belt conveyor, and is sent under pressure to the nozzle part 13 by the compressed air of the compressor 11, and at the same time, water is supplied from the water source 9 to another water hose. It is sent to the nozzle part through 12 'and sprayed on the ground 1 together with the sprayed base material 3 to form the vegetation base layer 2. The vegetation base layer 2 described above has a vegetation base layer provided with a greening net on the surface thereof according to the intended use (Japanese Patent Publication No. 62-21937 “Patent No. 1416457”).
No. ”), wastewater treatment method (Japanese Patent Publication No. 62-1050,“ Patent No. 1396451 ”, (Japanese Patent Publication No. 1-4012,“ Patent No. 1522804 ”) and a log prone construction method (Japanese Patent Laid-Open No.
No. 2-182316).
【0021】[0021]
【発明の効果】本発明は上記の構成であるから、有機質
の公共下水汚泥や産業廃棄物や生活廃棄物に、高温のパ
ルプ滓を加えた後、醗酵及び熟成して粒状又は粉末化し
た得た堆肥により、従来植生基盤材として用いられてい
た、黒土や山砂又は外国産ピ−トモスを採取調達する必
要がなくなり、環境破壊の防止と品質の安定が図れ、且
つ施工コストの低減を図ることができる。EFFECTS OF THE INVENTION Since the present invention has the above-mentioned constitution, after adding high temperature pulp slag to organic public sewage sludge, industrial waste and domestic waste, it is fermented and aged to obtain granules or powder. By eliminating compost, it is no longer necessary to collect and procure black soil, mountain sand, or foreign-produced peat moss, which were conventionally used as vegetation base materials, and to prevent environmental damage and stabilize quality, and reduce construction costs. be able to.
【0022】次に、本発明における堆肥には、パルプ滓
の焼却灰が混合されていることにより水分調整材の効果
及び醗酵促進並びに脱臭作用等の効果がある。すなわ
ち、パルプ滓の焼却灰は、含水量がきわめて少なく、水
分調整材として有効に発揮する。また、 100℃以上の高
温の焼却灰を低温の有機質汚泥や生活廃棄物若しくは産
業廃棄物と混合することによって、前記パルプの焼却熱
は熱交換作用で温度が下がるが、少なくとも60℃前後を
保持できるように設定したことにより、醗酵熱として利
用でき、醗酵の促進が図れることと、併せて従来では温
度調整のために用いていたガスバ−ナ−を使用しないで
済むから、そのガスバ−ナ−の炎が汚泥に触れてその近
傍の微生物を死滅させていたものが、その死滅を防止す
ることによって、醗酵や生産された基盤材用の堆肥効果
が高い。Next, the compost in the present invention is mixed with the incinerated ash of the pulp slag, and thus has the effect of a moisture conditioner, the effect of fermentation, and the effect of deodorizing. That is, the incinerated ash of pulp slag has an extremely low water content, and is effective as a moisture adjusting material. Also, by mixing high temperature incinerated ash of 100 ° C or higher with low temperature organic sludge, domestic waste or industrial waste, the heat of incineration of the pulp is lowered by heat exchange action, but at least around 60 ° C is maintained. By setting it so that it can be used as fermentation heat, the fermentation can be promoted, and at the same time, it is not necessary to use the gas burner conventionally used for temperature control, so the gas burner Although the flames of No. 1 touched the sludge and killed the microorganisms in its vicinity, the composting effect for fermentation and produced base materials is high by preventing the killing of the microorganisms.
【0023】さらに、パルプ滓の焼却灰は、焼却炉から
取出して間もない高温の状態で大量に使用するから、パ
ルプ滓の焼却灰の廃棄処理が不要となり、その廃棄処理
のための一時貯溜設備の設置や人手が不要となって一石
二鳥の効果がある。Further, since the incinerator ash of pulp slag is used in large quantities in a high temperature state immediately after being taken out from the incinerator, it is not necessary to dispose of the ash of pulp slag, and the temporary storage for the disposal is performed. There is no need to install equipment or manpower, and the effect of two birds with one stone is achieved.
【0024】また、パルプ滓の焼却灰は、有機炭素が10
%から15%程度含まれているので、脱臭作用や重金属等
非健康物質の吸着による流失防止作用および緑化の基盤
材としての有効性を高めることなど、粉炭と同様な効果
があるので、別途に粉炭を混入する必要がない。In addition, the incineration ash of pulp slag contains 10% of organic carbon.
Since it contains about 15% to 15%, it has the same effect as dust coal, such as deodorizing effect, prevention of washout by adsorption of non-healthy substances such as heavy metals, and effectiveness as a base material for greening. No need to mix pulverized coal.
【0025】さらに、前記の堆肥にコンニャクの精製時
に生じる飛粉を混合して基盤材を作製し、その基盤材を
吹付機に投入し、コンプレッサの圧縮空気によるノズル
噴射時に水を加えて混合しながら、地表面に所定の厚さ
になるように吹付けることにより、法面緑化の基盤作り
は、一度施工すればよく、重金属類の蓄積濃縮はなくな
り、肥料の成分も植生には充足しているから緑地の育成
に最適である。Further, the base material is prepared by mixing the above-mentioned compost with the flying powder produced during the purification of konjak, and the base material is put into a spraying machine, and water is added and mixed when the nozzle is jetted by the compressed air of the compressor. However, by spraying on the ground surface to a predetermined thickness, it is only necessary to construct the foundation for slope greening once, there is no accumulation and concentration of heavy metals, and the components of fertilizer are sufficient for vegetation. Because it is, it is ideal for growing green areas.
【0026】そして、基盤材を形成するのに従来のよう
に、山砂及び黒土又は土壌改良材としてピ−トモス及び
その類似物の使用の代わりに、有機質の下水汚泥その他
の廃棄物に対して、通気性を有して酸素供給が十分に行
われるパルプ滓の焼却灰を加えて醗酵・熟成して堆肥を
作製し、これにコンニャクの飛粉を加えることによって
得られる。そして、前記の基盤材をモルタル吹付機に投
入して混合し、そのノズル噴射機械を用いて、そのノズ
ル噴射時に水を混合しながら法面に所定の厚さに吹付け
ることにより、緑化に有効な基盤層が得られる。And instead of the conventional use of mountain sand and black soil or of peat moss and its analogues as soil conditioner to form the base material, for organic sewage sludge and other wastes. It is obtained by adding combusted manure by adding incinerated ash of pulp dregs that has air permeability and sufficient oxygen supply, fermenting and aging to make compost, and adding konjak fly powder. Then, the above-mentioned base material is put into a mortar spraying machine and mixed, and the nozzle spraying machine is used to spray water to a predetermined thickness on the slope while mixing water at the time of spraying the nozzles, which is effective for greening. An excellent base layer can be obtained.
【0027】しかも、有機質の産業廃棄物、生活廃棄物
を法面緑化工事における植生基盤の形成に有効利用でき
ることはもち論のこと、公共下水道から発生する生汚泥
の処理も無駄なく消化することができる。しかも、それ
らの廃棄処分に困窮していた問題も解決し、用途の拡大
も図れ、この種のリサイクル緑化基盤形成方法として新
規有益である。In addition, organic industrial waste and domestic waste can be effectively used for forming a vegetation base in slope greening work, and it is possible to digest waste sludge generated from public sewers without waste. it can. In addition, the problems that were difficult to dispose of can be solved, the applications can be expanded, and this is a new useful method for forming a recycling greening foundation of this kind.
【図1】基盤材生産プラント図である。FIG. 1 is a diagram of a base material production plant.
【図2】パルプ滓の焼却灰を得る処理工程を示す系統図
である。FIG. 2 is a system diagram showing a treatment process for obtaining incinerated ash of pulp dregs.
1 地山 2 植生基盤層 3 基盤材 4 堆肥 5 飛粉 6 有機質の廃棄物 7 パルプ滓の焼却灰 8 醗酵機 9 混合機 10 吹付機 11 コンプレッサ− 12 吹付ホ−ス 13 ノズル部(1) 1 Ground 2 Vegetation base layer 3 Base material 4 Compost 5 Flying powder 6 Organic waste 7 Incinerator ash of pulp dregs 8 Fermenter 9 Mixer 10 Sprayer 11 Compressor 12 Spraying hose 13 Nozzle part (1)
【表1】 (2)[Table 1] (2)
【表2】 (3)[Table 2] (3)
【表3】 [Table 3]
Claims (1)
は産業廃棄物に焼却炉から取出して間もない高温のパル
プ滓の焼却灰を加えて60℃前後を保持した後、醗酵・熟
成して粒状又は粉末化した堆肥を生産し、この堆肥にコ
ンニャクの精製時に生じる飛粉を混合して基盤材を作製
し、その基盤材を吹付機に投入し、コンプレッサの圧縮
空気によるノズル噴射時に水を加えて混合しながら、地
表面に所定の厚さの基盤層になるように吹付けることを
特徴とするリサイクル緑化基盤形成工法。1. An organic sewage sludge or domestic or industrial waste is added with incinerator ash of a high temperature pulp slag that has just been taken out from an incinerator, and the mixture is maintained at about 60 ° C., then fermented and aged to be granulated. Alternatively, a compost that has been pulverized is produced, and the base material is prepared by mixing the compost with the flying powder generated during the purification of konjak, and the base material is put into a spraying machine, and water is added when the nozzle is jetted by the compressed air of the compressor. A method for forming a recycle greening base, which consists of spraying so that a base layer with a predetermined thickness is sprayed onto the ground surface while mixing and mixing.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP41496590A JPH0678630B2 (en) | 1990-12-26 | 1990-12-26 | Recycling greening base formation method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP41496590A JPH0678630B2 (en) | 1990-12-26 | 1990-12-26 | Recycling greening base formation method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH04261914A JPH04261914A (en) | 1992-09-17 |
| JPH0678630B2 true JPH0678630B2 (en) | 1994-10-05 |
Family
ID=18523383
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP41496590A Expired - Fee Related JPH0678630B2 (en) | 1990-12-26 | 1990-12-26 | Recycling greening base formation method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0678630B2 (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2652114B2 (en) * | 1992-11-10 | 1997-09-10 | 上毛緑産工業株式会社 | Method for promoting fermentation of organic sludge |
| JPH07172967A (en) * | 1993-01-19 | 1995-07-11 | Jiyoumou Riyokusan Kogyo Kk | Method for promoting fermentation of organic sludge |
| KR100491497B1 (en) * | 2002-11-11 | 2005-05-27 | 트랜스코리아개발 주식회사 | Method of producing green ground |
-
1990
- 1990-12-26 JP JP41496590A patent/JPH0678630B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH04261914A (en) | 1992-09-17 |
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