JPH0445613B2 - - Google Patents
Info
- Publication number
- JPH0445613B2 JPH0445613B2 JP28731188A JP28731188A JPH0445613B2 JP H0445613 B2 JPH0445613 B2 JP H0445613B2 JP 28731188 A JP28731188 A JP 28731188A JP 28731188 A JP28731188 A JP 28731188A JP H0445613 B2 JPH0445613 B2 JP H0445613B2
- Authority
- JP
- Japan
- Prior art keywords
- spraying
- vegetation base
- slope
- fermentation
- forming
- 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
Links
- 239000000463 material Substances 0.000 claims description 63
- 239000000843 powder Substances 0.000 claims description 28
- 238000005507 spraying Methods 0.000 claims description 26
- 238000000855 fermentation Methods 0.000 claims description 21
- 230000004151 fermentation Effects 0.000 claims description 21
- 239000002440 industrial waste Substances 0.000 claims description 21
- 239000002361 compost Substances 0.000 claims description 20
- 238000000034 method Methods 0.000 claims description 20
- 239000010791 domestic waste Substances 0.000 claims description 19
- 239000010801 sewage sludge Substances 0.000 claims description 18
- 239000003610 charcoal Substances 0.000 claims description 13
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 13
- 238000002156 mixing Methods 0.000 claims description 9
- 239000004570 mortar (masonry) Substances 0.000 claims description 9
- 241001312219 Amorphophallus konjac Species 0.000 claims description 8
- 235000001206 Amorphophallus rivieri Nutrition 0.000 claims description 8
- 241000894006 Bacteria Species 0.000 claims description 8
- 229920002752 Konjac Polymers 0.000 claims description 8
- 235000010485 konjac Nutrition 0.000 claims description 8
- 239000000252 konjac Substances 0.000 claims description 8
- 238000007670 refining Methods 0.000 claims description 6
- 235000013312 flour Nutrition 0.000 claims description 3
- 230000008569 process Effects 0.000 claims description 3
- 239000003337 fertilizer Substances 0.000 description 13
- 239000002689 soil Substances 0.000 description 11
- 238000010276 construction Methods 0.000 description 9
- 230000000694 effects Effects 0.000 description 9
- 239000010802 sludge Substances 0.000 description 8
- 239000000853 adhesive Substances 0.000 description 7
- 230000001070 adhesive effect Effects 0.000 description 7
- 239000004576 sand Substances 0.000 description 7
- 239000000126 substance Substances 0.000 description 7
- 239000002699 waste material Substances 0.000 description 7
- 238000003756 stirring Methods 0.000 description 6
- 235000013311 vegetables Nutrition 0.000 description 6
- 239000000835 fiber Substances 0.000 description 5
- 230000006872 improvement Effects 0.000 description 5
- 239000003415 peat Substances 0.000 description 5
- 239000007921 spray Substances 0.000 description 5
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 4
- 229910052760 oxygen Inorganic materials 0.000 description 4
- 239000001301 oxygen Substances 0.000 description 4
- 230000001681 protective effect Effects 0.000 description 4
- 230000007613 environmental effect Effects 0.000 description 3
- 239000008187 granular material Substances 0.000 description 3
- 244000005700 microbiome Species 0.000 description 3
- 239000010815 organic waste Substances 0.000 description 3
- 231100000331 toxic Toxicity 0.000 description 3
- 230000002588 toxic effect Effects 0.000 description 3
- 241000251468 Actinopterygii Species 0.000 description 2
- 241000196324 Embryophyta Species 0.000 description 2
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 2
- 230000002411 adverse Effects 0.000 description 2
- 230000006378 damage Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 229910001385 heavy metal Inorganic materials 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 2
- 229910052753 mercury Inorganic materials 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 230000002829 reductive effect Effects 0.000 description 2
- 239000010865 sewage Substances 0.000 description 2
- 238000004162 soil erosion Methods 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 229920003002 synthetic resin Polymers 0.000 description 2
- 239000000057 synthetic resin Substances 0.000 description 2
- 229910052725 zinc Inorganic materials 0.000 description 2
- 239000011701 zinc Substances 0.000 description 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- 239000004698 Polyethylene Substances 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 229910052785 arsenic Inorganic materials 0.000 description 1
- RQNWIZPPADIBDY-UHFFFAOYSA-N arsenic atom Chemical compound [As] RQNWIZPPADIBDY-UHFFFAOYSA-N 0.000 description 1
- 239000010426 asphalt Substances 0.000 description 1
- 230000008901 benefit Effects 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 238000010411 cooking Methods 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 239000000839 emulsion Substances 0.000 description 1
- 230000003203 everyday effect Effects 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 239000003925 fat Substances 0.000 description 1
- 238000007667 floating Methods 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 230000035784 germination Effects 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 235000013372 meat Nutrition 0.000 description 1
- 239000010813 municipal solid waste Substances 0.000 description 1
- 229930014626 natural product Natural products 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- 229910001562 pearlite Inorganic materials 0.000 description 1
- 230000000737 periodic effect Effects 0.000 description 1
- 230000035699 permeability Effects 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- -1 polyethylene Polymers 0.000 description 1
- 229920000573 polyethylene Polymers 0.000 description 1
- 229920002689 polyvinyl acetate Polymers 0.000 description 1
- 239000011118 polyvinyl acetate Substances 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 230000003449 preventive effect Effects 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 239000008262 pumice Substances 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 239000003516 soil conditioner Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000003440 toxic substance Substances 0.000 description 1
- 230000008016 vaporization Effects 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
Landscapes
- Pit Excavations, Shoring, Fill Or Stabilisation Of Slopes (AREA)
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は、人工的に造成された裸地や、無機質
で劣性土壌の岩盤等の法面を緑化して保護する、
いわゆる法面緑化工事に先立つて施工する植生基
盤の形成方法に関するもので、生活廃棄物及び産
業廃棄物のうち、特に公共の下水道から発生する
生汚泥の処理を有効に行うと共に、その生活廃棄
物や産業廃棄物を法面緑化工事における植生用の
基盤材して活用しようとするものである。[Detailed Description of the Invention] [Field of Industrial Application] The present invention is a method for protecting slopes such as artificially created bare land and bedrock of inorganic and recessive soil by greening it.
This relates to a method for forming a vegetation base that is constructed prior to so-called slope greening work, and it effectively treats domestic waste and industrial waste, especially raw sludge generated from public sewers, and The project aims to use industrial waste as base material for vegetation in slope greening work.
本出願人は、植生基盤を形成するための基盤材
に、肥料のほかに粘着材としてコンニヤクの飛粉
を配合し、これに水を加えて混合したスラリーを
法面に吹き付ける工法を提案した(特公昭54−
1364号及び特公昭60−46923号公報参照)。
The applicant has proposed a construction method in which the base material for forming a vegetation base is mixed with konjac powder as an adhesive in addition to fertilizer, and a slurry made by adding water to this is sprayed onto the slope ( Tokuko Showa 54-
1364 and Special Publication No. 60-46923).
上記の緑化基盤材としては、山砂若しくは黒土
が用いられ、これに肥料・粘着材等が配合されて
いる。前記の肥料は、石灰や化学肥料(粒状・固
形の高 化成肥料)が用いられる。粘着材として
混合するコンニヤクの飛粉も遅効性肥料として役
立つ。 Mountain sand or black soil is used as the above-mentioned greening base material, and fertilizers, adhesives, etc. are mixed therein. Lime and chemical fertilizers (granular and solid high chemical fertilizers) are used as the above-mentioned fertilizers. Konjac dust, which is mixed in as an adhesive, also serves as a slow-release fertilizer.
実際の施工に当たつては以上の諸材料のほか
に、さらに土壌改良材としてピートモス及びその
類似物を混合している。 In actual construction, in addition to the above-mentioned materials, peat moss and its similar substances are also mixed as a soil conditioner.
そこで、近時は有機質の下水汚泥又は生活廃棄
物若しくは産業廃棄物等を特殊の方法によつて粉
末にして堆肥材料に変え、これに粘着性物質を加
えて法面に所定の厚さに吹付けて植生基盤を形成
するという技術が開発されている。 Therefore, recently, organic sewage sludge, domestic waste, industrial waste, etc. are turned into powder using a special method, turned into compost material, a sticky substance is added to this material, and the material is sprayed onto the slope to a predetermined thickness. A technology has been developed to attach plants and form a vegetation base.
ところが、上記のピートモス及びその類似物は
輸入品であるためにコストが高い。そこで、これ
の代替材料が求められていたが、適当なものがな
かつたのが現状である。また、基盤材用の山砂に
は、品質に安定性がないために均一の施工効果が
得られない恐れがある。また、黒土は品質は安定
しているが、高価であると共に、品薄で調達が困
難である。そして、広大な施工場所での吹付け面
積と吹付け厚さによつて大量に用意する必要があ
り、それだけ調達に要する工事経費が掛かると共
に、黒土や山砂の採山は、緑化を破壊する原因に
もなる。
However, the above-mentioned peat moss and its analogues are expensive because they are imported products. Therefore, an alternative material has been sought, but at present there is no suitable material. Furthermore, the quality of mountain sand used as a base material is not stable, so there is a risk that a uniform construction effect may not be obtained. Furthermore, although the quality of black soil is stable, it is expensive and difficult to procure due to shortage. In addition, it is necessary to prepare a large quantity depending on the spraying area and spraying thickness in a vast construction site, which increases the construction cost required for procurement, and the extraction of black soil and mountain sand destroys the greenery. It can also be a cause.
一方、公共の下水等における生汚泥その他の生
活廃棄物又は産業廃棄物は、毎日必ず大量に発生
し、その廃棄又は焼却処理が環境破壊の防止との
関連で深刻な社会問題になつている。 On the other hand, raw sludge and other domestic or industrial wastes are generated in large quantities every day in public sewage systems, and their disposal or incineration has become a serious social problem in connection with the prevention of environmental destruction.
また、他方において、有機質の下水汚泥又は生
活廃棄物若しくは産業廃棄物等を特殊の方法によ
つて粉末の堆肥材料に変え、これに粘着性物質を
加えて法面に吹付けて植生基盤を形成すること
は、それら各種の廃棄物の処理ができると共に、
土壌改良材として有効に活用できる長所がある。
ところがその反面、前記の各種の廃棄物の中に
は、ごく微量ではあるが、水銀、鉛、砒素、亜
鉛、銅等の有毒なもの、又は有害な成分が含まれ
ている場合がある。従つて、法面に吹付けて形成
した植生基盤に含まれる、前記の有害成分が地中
に侵入して地質を破壊し、生物に多大の悪影響を
与える恐れがあるという課題があつた。 On the other hand, organic sewage sludge, domestic waste, industrial waste, etc. is converted into powdered compost material using a special method, and a sticky substance is added to this material and sprayed onto the slope to form a vegetation base. What we do is that we can process these various types of waste, and
It has the advantage of being effectively used as a soil improvement material.
However, on the other hand, the various wastes mentioned above may contain toxic substances or harmful components such as mercury, lead, arsenic, zinc, copper, etc., although in very small amounts. Therefore, there is a problem that the above-mentioned harmful components contained in the vegetation base formed by spraying on the slope surface may penetrate into the ground, destroy the geology, and have a great adverse effect on living things.
本発明は、従来の法面緑化工事における植生基
盤の形成に際して、土壌改良に係るピートモスや
山砂・肥料等の使用をなくし、下水汚泥又は生活
廃棄物若しくは産業廃棄物を粉末の堆肥材料とし
て活用し、さらに前記の廃棄物に含まれる有害物
質の流出を押さえて上記の課題を解決することを
目的とする。
The present invention eliminates the use of peat moss, mountain sand, fertilizer, etc. for soil improvement when forming a vegetation base in conventional slope greening work, and utilizes sewage sludge, domestic waste, or industrial waste as powdered compost material. Furthermore, it is an object of the present invention to solve the above-mentioned problems by suppressing the outflow of harmful substances contained in the wastes.
上記の目的を達成するために本発明の第1は、
法面緑化工事における植生基盤の形成方法におい
て、有機質の下水汚泥又は生活廃棄物若しくは産
業廃棄物を醗酵機械に投入し、これに多孔質の水
分調整材と醗酵菌とを加えた後、前記醗酵機械に
よつて醗酵させた粒状化又は粉末化した堆肥と、
有機質の下水汚泥又は生活廃棄物若しくは産業廃
棄物を焼却処理して粒状化又は粉末化した焼却灰
を加え、その中にコンニヤク粉の精製時に生じる
飛粉と、木炭粉を加えて混合し、モルタル吹付機
械を用いて、そのノズル噴射時に水を混合しなが
ら法面に所定厚さの基盤材になるように吹付ける
ものである。 In order to achieve the above object, the first aspect of the present invention is to
In a method for forming a vegetation base in slope greening work, organic sewage sludge or domestic waste or industrial waste is put into a fermentation machine, a porous moisture control material and fermentation bacteria are added thereto, and then the fermentation process is carried out. Granulated or powdered compost fermented by a machine,
Granulated or powdered incineration ash obtained by incinerating organic sewage sludge, domestic waste, or industrial waste is added, and the flying powder produced during the refining of konjac flour and charcoal powder are added and mixed to form a mortar. A spraying machine is used to spray the base material onto the slope surface to a predetermined thickness while mixing water with the nozzle.
また、本発明の第2は、前記第1の発明に係る
法面緑化工事における植生基盤の形成方法におい
て、下面に養生材と種子を備えたネツト体を基盤
材の表面に密接的に張り巡らしたものである。 Further, the second aspect of the present invention is the method for forming a vegetation base in slope greening work according to the first invention, in which a net body having a curing material and seeds on the lower surface is closely stretched over the surface of the base material. It is something that
さらに、本発明の第3は、前記第1の発明に係
る法面緑化工事における植生基盤の形成方法にお
いて、基盤材の表面に種子吹付け工を行うもので
ある。 Furthermore, the third aspect of the present invention is the method for forming a vegetation base in slope greening work according to the first aspect, in which the surface of the base material is sprayed with seeds.
上記手段に基づく作用を説明すると、植生用の
基盤材は次の要領で作製する。すなわち、有機質
の下水汚泥又は生活廃棄物若しく産業廃棄物を醗
酵機械に投入し、これに多孔質の水分調整材と醗
酵菌を加えた後、前記醗酵機械によつて醗酵させ
粒状又は粉末化したて堆肥を作り、その堆肥を基
盤材として用い、同時にこれが肥料にもなるもの
である。
To explain the effect based on the above means, the base material for vegetation is produced in the following manner. That is, organic sewage sludge, domestic waste, or industrial waste is put into a fermentation machine, a porous moisture control material and fermentation bacteria are added thereto, and then fermented by the fermentation machine to form granules or powder. Freshly made compost is used as a base material, and at the same time, it can also be used as fertilizer.
また、有機質の下水汚泥又は生活廃棄物若しく
は産業廃棄物を焼却処理して粒状化又は粉末化し
た焼却灰は、山砂と同様に保水性、透水性の効果
があり、酸素供給の役割を果たすと共に、有機質
肥料や堆肥の肥効を促進する機能を有する。 In addition, incineration ash, which is granulated or powdered by incinerating organic sewage sludge, domestic waste, or industrial waste, has water retention and permeability effects similar to mountain sand, and plays a role in oxygen supply. It also has the function of promoting the fertilizing effect of organic fertilizers and compost.
さらに、飛粉は、粘着材として土壌の浸食防止
及び肥料として機能する。 Furthermore, the flying powder functions as an adhesive to prevent soil erosion and as a fertilizer.
そして、木炭粉は、土壌改良資材としての使用
目的のほかに、本発明の中では、特に有機質の下
水汚泥又は生活廃棄物若しくは産業廃棄物を醗酵
処理した堆肥と、焼却した焼却灰を植生基盤材基
盤材として利用することから、それらの中に微量
ではあるが含まれている有毒成分又は有害成分を
木炭粉に吸着されて流出防止として機能する。 In addition to the purpose of using charcoal powder as a soil improvement material, in the present invention, charcoal powder is particularly used as compost made by fermenting organic sewage sludge, domestic waste, or industrial waste, and incinerated incineration ash as a vegetation base. Since charcoal is used as a base material, the toxic or harmful components contained therein, although in trace amounts, are adsorbed by the charcoal powder and function as a preventive measure against outflow.
前記の堆肥、焼却灰及び粘着材並びに木炭粉
は、攪拌混合した後、モルタル吹付機械に入れて
当該機械のノズルを用いて、その噴射時に水と混
合しながら法面に、植栽又は種子吹付けに適する
所定厚さになるように吹付けることによつて植生
基盤を形成する。 The above-mentioned compost, incineration ash, adhesive material, and charcoal powder are stirred and mixed, then put into a mortar spraying machine, and using the nozzle of the machine, they are mixed with water during spraying and are used for planting or seed spraying on slopes. A vegetation base is formed by spraying to a predetermined thickness suitable for application.
前記の植生基盤の表面に養生材と種子を具備し
たネツト体を密接的に張り巡らす場合は、合成樹
脂製ネツト体の下面に養生材を形成する植物性の
粗繊維質を所定の厚さに敷き、これに種子を落ち
ないように絡ませておき、アンカーを用いてネツ
トの適宜位置を打ち付けて基盤材に密接するよう
に固定させる。 When a net containing a curing material and seeds is closely stretched over the surface of the vegetation base, the crude vegetable fibers forming the curing material are placed on the underside of the synthetic resin net to a predetermined thickness. Spread the netting, entangle the seeds with it so that they do not fall, and use anchors to secure the nets at appropriate locations so that they are tightly attached to the base material.
また、基盤材の表面に種子吹付けを行う場合
は、種子を水とフアイバーを可とする保護材と共
に攪拌機で混合した後、吹付機械によつて基盤材
の表面に吹付ける。 When spraying seeds onto the surface of the base material, the seeds are mixed with water and a fiber-compatible protective material using a stirrer, and then sprayed onto the surface of the base material using a spraying machine.
以下、本発明に係る法面緑化工事における植生
基盤の形成方法の実施例を図面を以て説明する。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Examples of the method for forming a vegetation base in slope greening work according to the present invention will be described below with reference to the drawings.
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・魚等の調理屑、その他の生ゴ
ミ類、さらに産業廃棄物は、多量の魚・畜肉類の
アラ、食品加工残滓等である。 Sewage sludge is mainly composed of sludge and other raw sludge generated from public sewers, and domestic waste is
Household cooking scraps such as vegetables and fish, other garbage, and industrial waste include a large amount of fish and meat scraps and food processing residue.
多孔質の水分調整材は、有機性廃棄物のうち、
含水率の高い下水汚泥にあつては、その含水率を
低くするために用いるものであつて、具体的に
は、前記の焼却灰、軽石を砕いた粒状物、セラミ
ツクス、パーライトのような焼成加工製品、植物
性の製品等を用いる。 Among organic waste, porous moisture control material
In the case of sewage sludge with a high moisture content, it is used to lower the moisture content, and specifically, the above-mentioned incineration ash, granular materials obtained by crushing pumice, ceramics, and calcination processing such as pearlite are used. products, plant-based products, etc.
醗酵菌は、一定の条件、すなわち水分・温度・
酸素の3条件を充足すると微生物が最も活躍しや
すい状況を作り出すことができる。例えば、まず
水分は55%〜60%に調整・脱水し、温度は55℃〜
65℃に保つた状態にしておく。そして、前記の条
件の下で有機性の廃棄物に混入すると、水分や油
脂分を分解気化しながら急速に増殖し、且つ醗酵
現象を発生させる性質を有している。また酸素
は、定時的な攪拌をすることによつて十分に供給
を継続するようになつている。 Fermenting bacteria thrive under certain conditions, namely moisture, temperature,
Satisfying the three oxygen conditions can create conditions in which microorganisms are most likely to thrive. For example, first, the moisture content is adjusted to 55% to 60% and dehydrated, and the temperature is 55℃ to 55℃.
Keep it at 65℃. When mixed into organic waste under the above conditions, it rapidly multiplies while decomposing and vaporizing water and fats and oils, and has the property of causing a fermentation phenomenon. Furthermore, sufficient oxygen supply is maintained by periodic stirring.
基盤材の形成は、前記の下水汚泥・生活廃棄
物・産業廃棄物等の有機性廃棄物に多孔質の水分
調整材と醗酵菌とを醗酵機械に混入し、且つ攪拌
して所定の時間を経過させることにより、当初の
含水率より低い含水率の堆肥ができ上がる。この
堆肥に有機質の下水汚泥又は生活廃棄物若しくは
産業廃棄物を焼却処理して粒状化又は粉末化した
焼却灰を加え、その中にコンニヤク粉の精製時に
生じる飛粉と木炭粉を加えて混合し、モルタル吹
付機械を用いて、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の基盤材になるように吹
付ける。 The base material is formed by mixing the organic waste such as sewage sludge, domestic waste, industrial waste, etc. with a porous moisture control material and fermentation bacteria in a fermentation machine, stirring it, and fermenting it for a predetermined period of time. By allowing the time to pass, compost with a lower moisture content than the initial moisture content is created. Granulated or powdered incineration ash obtained by incinerating organic sewage sludge, domestic waste, or industrial waste is added to this compost, and the flying powder and charcoal powder produced during the refining of konjac powder are added and mixed. Using a mortar spraying machine, the mortar is sprayed onto the slope to form a base material of a predetermined thickness while mixing water with the nozzle.
前記の基盤材の形成時に用いる飛粉は、土壌の
浸食を防止する粘着材の機能と肥料の機能を有す
るもので、ピーエムザイ(登録商標)と称する、
コンニヤク粉の精製時に生じる粉末を最も可とす
るが、前記の機能を有する植物性であれば、これ
に類する粉状若しくは顆粒状でもよい。 The flying powder used in forming the base material has the function of an adhesive to prevent soil erosion and the function of a fertilizer, and is called PMC (registered trademark).
Powder produced during the refining of konjac flour is most suitable, but similar powder or granule forms may be used as long as they are vegetable-based and have the above-mentioned functions.
なお、法面緑化工事における植生基盤の形成方
法において、植生基盤層2の表面に種子付きネツ
トを張り巡らす工事においては、ネツト体3を形
成するポリエチレン又はこれに類似する材料で12
mm×12mm若しくは20mm×25mm程度のマス目上に植
物性粗繊維質の養生材4を敷きつめ、これに種子
5を落ちないように絡ませ、その養生材4・種子
5の側を下面に向けてネツト体3を法面1に吹付
け形成した植生基盤層2の表面に密接させて張設
する。 In addition, in the method of forming a vegetation base in slope greening work, when a net with seeds is stretched over the surface of the vegetation base layer 2, polyethylene or a similar material forming the net body 3 is used.
Spread the vegetable crude fiber curing material 4 on a square of about mm x 12 mm or 20 mm x 25 mm, entangle the seeds 5 with this so that they do not fall, and turn the sides of the curing material 4 and seeds 5 downward. The net body 3 is stretched in close contact with the surface of the vegetation base layer 2 formed by spraying on the slope 1.
また、法面緑化工事における植生基盤の形成方
法における、前記基盤層2の表面に種子吹付けを
行う場合は、攪拌層に水を入れ、次いで保護材、
任意に選定した種子の順に投入した後、攪拌しな
がらノズル噴射によつて植生基盤層2の表面に吹
付けて行う。 In addition, when spraying seeds on the surface of the base layer 2 in the method of forming a vegetation base in slope greening work, water is poured into the stirring layer, and then the protective material,
After randomly selected seeds are added in the order, they are sprayed onto the surface of the vegetation base layer 2 using a nozzle jet while stirring.
() 「基盤材の製造工程」
公共下水2000tonから含水率80〜85%の汚泥
が約1ton産出される。() ``Base material manufacturing process'' Approximately 1 ton of sludge with a moisture content of 80-85% is produced from 2,000 ton of public sewage.
上記の汚泥を既存の醗酵機械に投入し、さら
に、多孔質の水分調整材及び醗酵菌とを前記醗
酵機械に投入して混合する。前記の混合物の量
に応じて8〜100時間を経過すると、前記の汚
泥が醗酵して含水率が20%に減少して、ある程
度に乾燥化した堆肥が得られる。 The above-mentioned sludge is put into an existing fermentation machine, and then a porous moisture control material and fermentation bacteria are put into the fermentation machine and mixed. After 8 to 100 hours, depending on the amount of the mixture, the sludge is fermented and its moisture content is reduced to 20%, yielding a somewhat dry compost.
前記の堆肥と、有機質の下水汚泥又は生活廃
棄物若しくは産業廃棄物を焼却処理して粒状化
又は粉末化した焼却灰を加え、その中にコンニ
ヤク粉の精製時に生じる飛粉と、木炭粉を加え
て混合し、モルタル吹付機械を用いて、そのノ
ズル噴射時に水を混合しながら法面に所定の厚
さの基盤層になるように吹付ける。 Add the above-mentioned compost and granulated or powdered incineration ash obtained by incinerating organic sewage sludge, domestic waste, or industrial waste, and add the flying powder produced during the refining of konjac powder and charcoal powder to it. Then, using a mortar spraying machine, spray the mortar onto the slope surface to form a base layer of a predetermined thickness while mixing water with the nozzle.
() 「植生基盤の施工例」
次に本発明による植生基盤の施工例を説明する
と、まず、植生基盤を形成するための配合割合の
一例は次の通りである。() "Example of Construction of Vegetation Base" Next, an example of construction of the vegetation base according to the present invention will be described. First, an example of the blending ratio for forming the vegetation base is as follows.
・ 吹付け面積 100.0m2
・ 吹付け厚さ 5.0cm
・ 基盤材(堆肥) 3.6m3
(焼却灰) 5.4m3
・ 飛粉(ピーエムザイ=登録商標) 135.0Kg
・ 木炭粉 350.0Kg
・ 肥料(コーテイング肥料) 10.0Kg
そして、上記の配合割合による工事にあたつて
は、あらかじめ法面1の浮石や木片等を除去して
おく。・ Spraying area 100.0m 2・ Spraying thickness 5.0cm ・ Base material (compost) 3.6m 3 (Incineration ash) 5.4m 3・ Flying powder (PMZI = registered trademark) 135.0Kg ・ Charcoal powder 350.0Kg ・ Fertilizer (coating) Fertilizer) 10.0Kg When carrying out construction using the above mixing ratio, floating stones, wood chips, etc. from slope 1 should be removed in advance.
次に、前記の材料をベルトコンベヤ又はシヨベ
ル等によつて既存のモルタル吹付機械に投入し、
コンプレツサの圧搾空気を送つて噴射ノズルによ
る吹付けを開始する。このとき、動力噴霧機から
送られてくる水(使用量は前記基盤材料に対して
1500〜2100)をノズル部で加えて混合しながら
法面1に略均一に吹付けて所定の厚さの植生基盤
層2を形成するものである。 Next, the above materials are introduced into an existing mortar spraying machine using a belt conveyor, shovel, etc.
Send compressed air from the compressor and start spraying from the injection nozzle. At this time, water sent from the power sprayer (the amount used is based on the base material)
1,500 to 2,100) is added to the nozzle portion and sprayed substantially uniformly onto the slope surface 1 while mixing to form a vegetation base layer 2 of a predetermined thickness.
そして、上記植生基盤層2の表面に緑化ネツト
工を施す場合は次の要領で行う。 When a greening net work is applied to the surface of the vegetation base layer 2, it is performed in the following manner.
・ ネツト体(養生材付) 120m2
(治山用12mm×12mm、20mm×25mm)
(一般用12mm×12mm、20mm×25mm)
・ 種子 1.0Kg
(ケンタツキ−31−フエスク、クリーンピン
グレツドその他)
・ アンカー(メイン) 15本
・ 補助アンカー(目串) 300本
上記のネツト体3に植物性の粗繊維質から成る
養生材4を敷き、これに種子5を脱落しないよう
に絡ませ、当該ネツト体を、その養生材・種子を
下に向けて法面1に形成した植生基盤層2の表面
に密接的に張設する。- Net body (with curing material) 120m 2 (12mm x 12mm, 20mm x 25mm for forest protection) (12mm x 12mm, 20mm x 25mm for general use) - Seeds 1.0Kg (Kentatsuki-31-Fuesk, Clean Pin Gretz, etc.) - Anchor (Main) 15 pieces / Auxiliary anchors (mesh skewers) 300 pieces A curing material 4 made of vegetable coarse fiber is spread on the net body 3 described above, and the seeds 5 are entangled with this so as not to fall off, and the net body is The curing material/seeds are tightly placed on the surface of the vegetation base layer 2 formed on the slope 1, facing downward.
また、上記植生基盤層2に対する種子吹付け工
においては、水→保護材(フアイバ)→種子の順
に攪拌槽に投入し、攪拌しながら吹付機械の噴射
ノズルで植生基盤層2の表面にムラなく吹付け
る。 In addition, in the seed spraying process for the vegetation base layer 2, water → protective material (fiber) → seeds are poured into a stirring tank in the order of water, and while stirring, the spray nozzle of the spraying machine is applied to the surface of the vegetation base layer 2 evenly. Spray.
本発明は上記の構成であるから、請求項1記載
の法面緑化工事における植生基盤の形成方法にお
いて、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ートモス及びそ
の類似物を使用を代わりに、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
が十分に行われる多孔質の水分調整材と醗酵菌と
を加えて醗酵させて堆肥を作り、この堆肥に有機
質の下水汚泥又は生活廃棄物又は産業廃棄物を焼
却処理して粒状又は粉末化した焼却灰を加え、そ
の中にコンニヤク粉の精製時に生じる飛粉と、木
炭粉を加えて混合し、モルタル吹付機械を用い
て、そのノズル噴射時に水を混合しながら法面に
所定の厚さの基盤材になるように吹付けることに
よつて土壌改良が成され、従来は必ず必要とされ
ていた山砂及びピートモス又はその類似物並びに
従来使用していたポリ酢酸ビニールやアスフアル
ト乳剤等の化学質性粘着材が不要となり、公害に
繋がる廃棄物の有効利用及び環境保護の維持並び
に植生基盤の製作コストの大幅な低減が図れる。
Since the present invention has the above configuration, in the method for forming a vegetation base in slope greening work according to claim 1, mountain sand and black soil or peat moss as a soil improvement material can be used to form the base material as conventionally. Instead of using similar products, organic sewage sludge and other wastes are fermented by adding fermentation bacteria and a porous moisture control material that is breathable and provides sufficient oxygen supply. Compost is made, and granulated or powdered incineration ash obtained by incinerating organic sewage sludge, domestic waste, or industrial waste is added to this compost, and the flying powder produced during the refining of konjac powder and charcoal powder are added to the compost. Soil improvement is accomplished by mixing the mixture and using a mortar spraying machine to mix water into the nozzle and spray it onto the slope to form a base material of a predetermined thickness. This eliminates the need for mountain sand, peat moss, or similar materials, as well as chemical adhesives such as polyvinyl acetate and asphalt emulsion, which were previously used, making the effective use of waste that can lead to pollution and the maintenance of environmental protection possible. The production cost of the vegetation base can be significantly reduced.
また、有機質の生活廃棄物・産業廃棄物を自然
醗酵させると、通常は2年掛かるが、本発明のよ
うに醗酵機械に多孔質の水分調整材と醗酵菌を前
記の廃棄物に加えて醗酵させることによつて、含
水率が均一な堆肥が得られる。 In addition, it usually takes two years to naturally ferment organic household waste and industrial waste, but as in the present invention, a porous moisture control material and fermentation bacteria are added to the waste in a fermentation machine to carry out fermentation. By doing so, compost with uniform moisture content can be obtained.
さらに、緑化に必要な土壌内部の微生物を醗酵
の段階で多量に使用するので出来上がつた堆肥に
は多くの微生物が含まれている。従つて、自然の
客士と殆ど同等な品質が得られる。 Furthermore, since a large amount of the microorganisms inside the soil necessary for greening are used in the fermentation stage, the resulting compost contains many microorganisms. Therefore, it is possible to obtain a quality almost equivalent to that of a natural product.
そして、基盤材に混合されている木炭粉は、そ
の性質として吸着性が強く且つ1g当たり200〜
300m2程度の広い吸着面積を有することにより、
法面に吹付施工された植生基盤層中に水銀や亜鉛
等の重金属を始めとする微量ではあるが有毒成分
又は有害成分が含有していたとしても、その木炭
粉でその重金属類その他の有毒・有害の成分を確
実に吸着して外部への流出を抑えることができ
る。これによつて、地質の破壊や生物への悪影響
が取り除かれ、環境保全の効果がある。 The charcoal powder mixed into the base material has strong adsorption properties and 200 to 200 g/g.
By having a large adsorption area of about 300m2 ,
Even if the vegetation base layer sprayed onto the slope contains trace amounts of toxic or harmful components, such as heavy metals such as mercury or zinc, the charcoal powder will remove the heavy metals and other toxic and harmful components. It can reliably adsorb harmful components and prevent them from leaking outside. This eliminates geological destruction and adverse effects on living things, and has the effect of environmental conservation.
而も、公共の下水汚泥、有機質の生活廃棄物・
産業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、この種の法面緑化工事における植
生基盤の形成方法として新規有益である。 Moreover, public sewage sludge, organic domestic waste,
It goes without saying that industrial waste can be effectively used to form a vegetation base in slope greening work, and raw sludge generated from public sewers can also be digested without waste, making it possible to effectively use industrial waste to form a vegetation base in slope greening work. It is novel and useful as a method of forming a foundation.
なお、請求項2記載の植生基盤層にネツト体を
張設したものにおいては、基盤層に確実に根活着
し、発芽するまで保護材で被覆して雨水からの流
失を確実に防止する。 In addition, in the structure in which the net body is stretched over the vegetation base layer according to claim 2, the roots are securely attached to the base layer and covered with a protective material until they germinate to reliably prevent runoff from rainwater.
また、請求項3記載の植生基盤層に種子を吹付
ける工法においては、堆肥による基盤層に種子が
よく馴染み、根活着が安定して発芽生育の歩留り
が良好である。 In addition, in the method of spraying seeds onto a vegetation base layer according to claim 3, the seeds are well adapted to the base layer of compost, stable root establishment is achieved, and the yield of germination and growth is good.
図面は本発明に係る法面緑化工事における植生
基盤形成方法の実施例を示すもので、第1図は基
盤材生産プラント図、第2図は作業工程状態示す
法面の縦断側面図、第2図施工法面の拡大縦断面
図、第3図は養生材・種子付きネツト体の一部を
上向き状態にして示す斜視図である。
1……法面、2……植生基盤層、3……合成樹
脂製ネツト体、4……植物性の粗繊維質から成る
養生材、5……種子。
The drawings show an example of the method for forming a vegetation base in slope greening work according to the present invention. FIG. 3 is an enlarged vertical sectional view of the construction slope, and FIG. 3 is a perspective view showing a part of the net with curing material and seeds facing upward. 1...Slope surface, 2...Vegetation base layer, 3...Synthetic resin net body, 4...Curing material made of vegetable crude fiber, 5...Seeds.
Claims (1)
業廃棄物を醗酵機械に投入し、これに多孔質の水
分調整材と醗酵菌とを加えた後、前記醗酵機械に
よつて醗酵させた粒状化又は粉末化した堆肥と、
有機質の下水汚泥又は生活廃棄物若しくは産業廃
棄物を焼却処理して粒状化又は粉末化した焼却灰
を加え、その中にコンニヤク粉の精製時に生じる
飛粉と、木炭粉を加えて混合し、モルタル吹付機
械を用いて、そのノズル噴射時に水を混合しなが
ら法面に所定厚さの基盤層になるように吹付ける
ことを特徴とする法面緑化工事における植生基盤
の形成方法。 2 下面に養生材と種子を備えたネツト体を基盤
材の表面に密接的に張り巡らしたことを特徴とす
る請求項1記載の法面緑化工事における植生基盤
の形成方法。 3 基盤材の表面に種子吹付け工を行うことを特
徴とする請求項1記載の法面緑化工事における植
生基盤の形成方法。[Scope of Claims] 1. Organic sewage sludge, domestic waste, or industrial waste is put into a fermentation machine, a porous moisture control material and fermentation bacteria are added thereto, and then fermentation is carried out by the fermentation machine. granulated or powdered compost;
Granulated or powdered incineration ash obtained by incinerating organic sewage sludge, domestic waste, or industrial waste is added, and the flying powder produced during the refining of konjac flour and charcoal powder are added and mixed to form a mortar. A method for forming a vegetation base in slope greening work, characterized by using a spraying machine and spraying the slope surface to form a base layer of a predetermined thickness while mixing water when spraying the nozzle. 2. The method for forming a vegetation base in slope greening work according to claim 1, characterized in that a net body having a curing material and seeds on the lower surface is closely stretched over the surface of the base material. 3. The method for forming a vegetation base in slope greening work according to claim 1, characterized in that a seed spraying process is performed on the surface of the base material.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP28731188A JPH02132227A (en) | 1988-11-14 | 1988-11-14 | Method for forming vegitation base for slope-face tree-planting construction |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP28731188A JPH02132227A (en) | 1988-11-14 | 1988-11-14 | Method for forming vegitation base for slope-face tree-planting construction |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH02132227A JPH02132227A (en) | 1990-05-21 |
JPH0445613B2 true JPH0445613B2 (en) | 1992-07-27 |
Family
ID=17715729
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP28731188A Granted JPH02132227A (en) | 1988-11-14 | 1988-11-14 | Method for forming vegitation base for slope-face tree-planting construction |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH02132227A (en) |
-
1988
- 1988-11-14 JP JP28731188A patent/JPH02132227A/en active Granted
Also Published As
Publication number | Publication date |
---|---|
JPH02132227A (en) | 1990-05-21 |
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