JPH0723614B2 - Method of forming vegetation base in slope greening work - Google Patents
Method of forming vegetation base in slope greening workInfo
- Publication number
- JPH0723614B2 JPH0723614B2 JP63054292A JP5429288A JPH0723614B2 JP H0723614 B2 JPH0723614 B2 JP H0723614B2 JP 63054292 A JP63054292 A JP 63054292A JP 5429288 A JP5429288 A JP 5429288A JP H0723614 B2 JPH0723614 B2 JP H0723614B2
- Authority
- JP
- Japan
- Prior art keywords
- vegetation base
- slope
- fermentation
- machine
- compost
- 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 - Lifetime
Links
- 238000000034 method Methods 0.000 title claims description 12
- 239000000463 material Substances 0.000 claims description 38
- 238000000855 fermentation Methods 0.000 claims description 26
- 230000004151 fermentation Effects 0.000 claims description 26
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 23
- 239000002361 compost Substances 0.000 claims description 20
- 238000005507 spraying Methods 0.000 claims description 17
- 241000894006 Bacteria Species 0.000 claims description 13
- 238000010276 construction Methods 0.000 claims description 10
- 239000010801 sewage sludge Substances 0.000 claims description 10
- 239000002440 industrial waste Substances 0.000 claims description 9
- 238000004065 wastewater treatment Methods 0.000 claims description 9
- 239000010791 domestic waste Substances 0.000 claims description 8
- 238000002156 mixing Methods 0.000 claims description 7
- 239000004570 mortar (masonry) Substances 0.000 claims description 6
- 239000002023 wood Substances 0.000 claims description 3
- 206010016807 Fluid retention Diseases 0.000 claims description 2
- 239000003337 fertilizer Substances 0.000 description 11
- 239000002689 soil Substances 0.000 description 11
- 239000002699 waste material Substances 0.000 description 11
- 239000010865 sewage Substances 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 5
- 239000000126 substance Substances 0.000 description 4
- 241000196324 Embryophyta Species 0.000 description 3
- 229920002752 Konjac Polymers 0.000 description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 230000006872 improvement Effects 0.000 description 3
- 235000010485 konjac Nutrition 0.000 description 3
- 244000005700 microbiome Species 0.000 description 3
- 239000010815 organic waste Substances 0.000 description 3
- 229910052760 oxygen Inorganic materials 0.000 description 3
- 239000001301 oxygen Substances 0.000 description 3
- 239000000843 powder Substances 0.000 description 3
- 235000013311 vegetables Nutrition 0.000 description 3
- 241000251468 Actinopterygii Species 0.000 description 2
- 241001465754 Metazoa Species 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- 239000011248 coating agent Substances 0.000 description 2
- 238000000576 coating method Methods 0.000 description 2
- 239000003415 peat Substances 0.000 description 2
- 239000008262 pumice Substances 0.000 description 2
- 239000011435 rock Substances 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- 239000004575 stone Substances 0.000 description 2
- 239000000758 substrate Substances 0.000 description 2
- 241001312219 Amorphophallus konjac Species 0.000 description 1
- 235000001206 Amorphophallus rivieri Nutrition 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 241000508723 Festuca rubra Species 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 239000010426 asphalt Substances 0.000 description 1
- 238000004364 calculation method Methods 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000010411 cooking Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000000839 emulsion Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000003925 fat Substances 0.000 description 1
- 239000000835 fiber 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
- 239000008187 granular material Substances 0.000 description 1
- 230000012010 growth Effects 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 239000000252 konjac Substances 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 235000013372 meat Nutrition 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000010813 municipal solid waste Substances 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- 239000010451 perlite Substances 0.000 description 1
- 235000019362 perlite Nutrition 0.000 description 1
- 230000035699 permeability Effects 0.000 description 1
- 230000008635 plant growth Effects 0.000 description 1
- 229920002689 polyvinyl acetate Polymers 0.000 description 1
- 239000011118 polyvinyl acetate Substances 0.000 description 1
- 230000001681 protective effect Effects 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000007226 seed germination Effects 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
- 241000894007 species Species 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 230000004083 survival effect Effects 0.000 description 1
- -1 temperature Substances 0.000 description 1
- 230000007704 transition Effects 0.000 description 1
- 230000008016 vaporization Effects 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、法面緑化工事に
先立って実施する植生基盤の形成方法に関するものであ
る。DETAILED DESCRIPTION OF THE INVENTION [Industrial field of application] The present invention is applicable to slope revegetation construction for protecting and protecting artificial slopes such as bare land and rocks of inorganic recessive soil. The present invention relates to a method of forming a vegetation base that is carried out in advance.
本出願人は、植生基板を形成するための緑化基盤材に、
肥料のほかに粘着材としてコンニャクの飛粉を配合し、
これに水を加えて混合したスラリーを法面に吹付ける工
法を提供した(特公昭54−1364号公報、特公昭60−4692
3号公報参照)。The applicant of the present invention, as a greening base material for forming a vegetation substrate,
In addition to fertilizer, konjak fly powder is mixed as an adhesive material,
A method of spraying slurry mixed with water on the slope was provided (Japanese Patent Publication No. 54-1364 and Japanese Patent Publication No. 60-4692).
(See publication 3).
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。山砂は施
工現場で比較的容易に調達できるもので軽石を含むもの
を使用する。肥料は石灰や化学肥料(粒状・固形の高度
化成肥料)が用いられる。粘着材として混合するコンニ
ャク飛粉も遅効性肥料として役立つ。As the above-mentioned greening base material, mountain sand or black soil is used, and a fertilizer, an adhesive material and the like are mixed therein. Mountain sand that contains pumice stone that can be procured relatively easily at the construction site is used. As the fertilizer, lime or chemical fertilizer (granular / solid advanced chemical fertilizer) is used. Konjac fly powder mixed as an adhesive also serves as a slow-acting fertilizer.
実際の施工にに当たっ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 the actual construction, in addition to the above materials, peat moss and its analogues are mixed as a soil conditioner.
ところが、上記のピートモス及びその類似物は輸入品で
あるためにコスト高である。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ったのが現状である。However, since the above-mentioned peat moss and its analogues are imported products, the cost is high. Therefore, a substitute material for this has been sought, but there is no suitable one at present.
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、土壌改良に係る上記の課題を解決することを目
的とする。An object of the present invention is to solve the above-mentioned problems relating to soil improvement when forming a vegetation base in conventional slope greening work.
そこで、上記の課題を解決し、且つ発明の目的を達成す
るために、本発明は第1の手段として、法面緑化工事に
おける植生基盤の形成方法に係り、崩壊法面、切取法面
を取水等による流失を防ぐための法面排水処理工におい
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、前記醗酵機械によって二次醗酵させ
て堆肥を作り、その堆肥をモルタル吹付機を用いてその
ノズル噴射時に水を混合しながら排水処理工法面及び排
水溝面に所定厚さになるように吹き付けて植生基盤を形
成し、前記植生基盤の表面に、種子及び種子用養生材を
備えたネット体を張り巡らしてアンカーで固定したもの
である。Therefore, in order to solve the above-mentioned problems and to achieve the object of the invention, the present invention relates to a method of forming a vegetation base in a slope greening work as a first means, in which a collapse slope and a cut slope are taken. In sloped wastewater treatment works to prevent washout due to etc., organic sewage sludge or domestic waste or industrial waste is put into a fermentation machine, and after adding a porous water-conditioning material and a fermentation bacterium, Secondary fermenting is performed by the fermentation machine to make compost, and the compost is sprayed with a mortar spraying machine while mixing water at the time of its nozzle spraying on the wastewater treatment method surface and drainage groove surface to a predetermined thickness and vegetation. A base is formed, and a net body including seeds and a seed curing material is stretched around the surface of the vegetation base and fixed by an anchor.
また、本発明のもう一つの手段は、法面緑化工事におけ
る植生基盤の形成方法に係り、緑化基盤の保水性を高
め、且つ安全を図るための間伐材利用による丸太伏せ工
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、前記醗酵機械によって二次醗
酵させて堆肥を作り、その堆肥をモルタル吹付機を用い
てそのノズル噴射時に水を混合しながら丸太伏せ工の隣
合丸太間の法面に所定厚さになるように吹き付けて植生
基盤を形成し、前記植生基盤の表面に、種子及び種子用
養生材を備えたネット体を張り巡らしてアンカーで固定
し、丸太伏せ工における丸太の直上部位に苗木を植栽し
たものである。Further, another means of the present invention relates to a method for forming a vegetation base in a slope greening work, in order to enhance water retention of the greening base and to secure safety, in a log felling work using thinned wood, organic sewage is used. Put sludge or domestic waste or industrial waste into a fermentation machine, add porous moisture control material and fermentation bacteria to it, make secondary ferment by the fermentation machine to make compost, and mortar the compost Using a spraying machine to form a vegetation base by spraying to a predetermined thickness on the slope between adjacent logs of a log felling work while mixing water at the time of jetting the vegetation base, on the surface of the vegetation base, seeds and A net body provided with a curing material for seeds is stretched around and fixed with an anchor, and a sapling is planted directly above the log in the log felling work.
〔作 用〕 上記手段に基づく作用を説明すると、まず本発明の第1
の手段にあっては、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、前記醗酵機械によっ
て二次醗酵させて作った堆肥を、モルタル吹付機械を用
いて法面排水処理工における法面、又は丸太伏せ工にお
ける隣合う丸太間の法面に吹き付けを行って所定厚さの
植生基盤を形成する。この場合、前記の植生基盤材は、
それ自体に適度の粘性を有しているので、水を加えて吹
き付けた後に乾燥すると、別途に粘着材を加えないでも
固まる作用がある。而も、同時に醗酵堆肥としての機能
も果たす。[Operation] The operation based on the above means will be described. First, the first aspect of the present invention
In the means, the organic sewage sludge or domestic waste or industrial waste is put into a fermentation machine, and after adding a porous moisture control material and a fermentation bacterium to the fermentation machine, the second fermentation is carried out by the fermentation machine. Using the mortar spraying machine, the compost produced in this way is sprayed on the slope in the slope drainage treatment work or the slope between the adjacent logs in the log felling work to form a vegetation base with a predetermined thickness. In this case, the vegetation base material is
Since it has an appropriate viscosity by itself, when water is added and sprayed and then dried, it has the action of hardening without adding an adhesive material separately. At the same time, it also functions as a fermenting compost.
また、本発明のもう一つの手段にあっては、前記第1の
手段によって形成した植生基盤の表面に種子及び種子用
養生材を下面に向けて備えたネット体を張り巡らしてア
ンカーで固定し、さらに丸太の直上部位に苗木を植栽し
て種子の発芽の促進と根の活着を確実化する。Further, in another means of the present invention, a net body having seeds and a seed curing material facing downward is stretched around the surface of the vegetation base formed by the first means and fixed with an anchor. In addition, plant seedlings directly above the logs to ensure seed germination and root survival.
次に本発明方法の実施例を説明する。第1図は法面緑化
工事の施工例を示す概略図、第2図〜第4図は排水処理
工を示し、第2図は正面図、第3図は第2図の3−3線
に沿う拡大断面図、第4図は第2図の4−4線に沿う拡
大断面図、第5図〜第7図は丸太伏せ工を示し、第5図
は正面図、第6図は第5図の6−6線に沿う拡大断面
図、第7図は第5図のa部の拡大断面図、第8図は植生
基盤の表面に張設する緑化ネット体の一部の斜視図であ
る。Next, examples of the method of the present invention will be described. Fig. 1 is a schematic diagram showing a construction example of slope greening work, Figs. 2 to 4 show wastewater treatment works, Fig. 2 is a front view, and Fig. 3 is a line 3-3 in Fig. 2. 4 is an enlarged sectional view taken along line 4-4 of FIG. 2, FIGS. 5 to 7 show a log bend operation, FIG. 5 is a front view, and FIG. 6 is a fifth section. Fig. 6 is an enlarged cross-sectional view taken along line 6-6, Fig. 7 is an enlarged cross-sectional view of portion a of Fig. 5, and Fig. 8 is a perspective view of a part of the greening net body stretched on the surface of the vegetation base. .
まず、植生基盤は土壌改良に欠かすことができないが、
その「土壌」とは、次のように考えられる。すなわち、
細粒岩質だけでなく、有機質成分を含み、またその中に
土壌動物,細菌類を含み、それらの働きで動物・植物の
遺体を分解して無機質の、植物の成育に必要な肥料分を
作り出す機能を備えていなければならない。そのため
に、今までの土壌基盤材に有機質の成分と、生態系の分
解者である細菌類を混入させて、より自然の土壌に近づ
けた、植生基盤材が、生態系の遷移の期間を短縮させ、
人工基盤材が短時間で、自然の生態系の中に溶け込むた
めに、より有用と思われる。First, the vegetation base is essential for soil improvement,
The "soil" is considered as follows. That is,
It contains not only fine-grained rocks but also organic components, and also soil animals and bacteria, which decompose the bodies of animals and plants to produce inorganic fertilizer components necessary for the growth of plants. Must have the ability to create. For that purpose, the vegetation base material, which is closer to natural soil by mixing organic components and bacteria that are decomposers of the ecosystem into the existing soil base material, shortens the transition period of the ecosystem. Let
It seems to be more useful because the artificial base material will quickly integrate into the natural ecosystem.
上記のように土壌改良をする植生基盤となる材料のう
ち、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、一般の家庭
から出る野菜・魚等の調理屑、その他の生ゴミ類であ
り、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。そして、前記の各種廃棄物は、
セラミックスを担体としてこれに醗酵菌を相当量加えて
加熱し、一定の温度に保った状態で送気撹拌する。これ
によって、植生基盤材は、醗酵堆肥として機能する。Of the materials that serve as vegetation bases for soil improvement as described above, sewage sludge is mainly sludge and other raw mud produced from public sewers, and domestic waste is vegetables and fish from ordinary households. Cooking wastes such as etc. and other raw garbage, and industrial wastes are large amounts of fish and meat ara,
Such as food processing residue. And the various wastes mentioned above
Using ceramics as a carrier, a considerable amount of fermenting bacteria is added and heated, and the mixture is fed and stirred while maintaining a constant temperature. As a result, the vegetation base material functions as fermented compost.
また、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っては、その含水率を低くする
ために用いるものであって、具体的には、軽石を砕いた
粒状物、セラミックス、パーライトのような焼成加工製
品を用いる。In addition, the porous moisture conditioner is used to reduce the water content of sewage sludge having a high water content among organic wastes. Specifically, pumice is crushed. Baking products such as granular materials, ceramics and perlite are used.
醗酵菌は、一定の条件、すなわち水分・温度・酸素の三
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℃に保った状態にしてお
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。Fermentation bacteria can create a situation in which microorganisms are most likely to play an active part if certain conditions, that is, water, temperature, and oxygen are satisfied. For example, first adjust the water content to 55% -60% and dehydrate it, and keep the temperature at 55-65 ° C. And when mixed with organic waste under the above conditions, it rapidly grows while decomposing and vaporizing water and fats and oils,
Moreover, it has the property of causing a fermentation phenomenon.
そして酸素は、定時的な攪拌をすることによって十分に
供給を継続するようになっている。Then, oxygen is supplied continuously by agitating at regular intervals.
(I)「植生基盤材の製造工程例」 公共下水2,000tonから含水率80〜85%の汚泥が約1ton産
出される。(I) “Example of vegetation base material manufacturing process” About 1 ton of sludge with a water content of 80 to 85% is produced from 2,000 ton of public sewage.
そこで第1図に示すように、有機質の下水汚泥・生活廃
棄物・産業廃棄物の有機性廃棄物に醗酵菌11と多孔質の
水分調整材12とをベルトコンベア14又はショベル等によ
って醗酵機械13に投入して攪拌する。前記の投入物の量
に応じて8〜100時間を経過すると、前記の汚泥が二次
醗酵して含水率が50%に減少して、ある程度にさらさら
しながらも多少粘り気のある粉末ないし粒状の堆肥物質
に変化する。Therefore, as shown in FIG. 1, fermentation bacterium 11 and porous moisture control material 12 are added to organic waste such as organic sewage sludge, domestic waste, and industrial waste by a belt conveyor 14 or a shovel or the like. And stir. After 8 to 100 hours depending on the amount of the above-mentioned input material, the sludge is secondarily fermented and the water content is reduced to 50%. Change to compost material.
上記醗酵処理を行う全自動処理装置が開発され実用に供
されており、大量の廃棄物を短い時間で処理でき、廃棄
物の容積は20〜10%まで縮小する。A fully automatic treatment device for performing the above fermentation treatment has been developed and put into practical use, and a large amount of waste can be treated in a short time, and the volume of waste can be reduced to 20 to 10%.
(II)「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。まず、
植生基盤を形成するための吹き付け面積及び厚さと必要
材料の割合は次の通りである。(II) “Example of construction of vegetation base” Next, an example of construction of the vegetation base according to the present invention will be described. First,
The ratio of required area and material for spraying area and thickness for forming vegetation base is as follows.
・吹付け面積 100m2 ・吹付け厚さ 5cm ・植生基板材(堆肥) 9m3 ・水 1500〜2100 前記の施工工事にあたっては、まず、法面1の浮石や木
片等を除去しておく。・ Spraying area 100m 2・ Spraying thickness 5cm ・ Vegetable substrate material (compost) 9m 3・ Water 1500 to 2100 In the above construction work, first remove the floating stones and wood chips on the slope 1.
上記植生基盤2の形成は、植生基盤材10をモルタル吹付
機15に投入して攪拌混合した後、コンプレッサ16から圧
搾空気と、動力噴霧機17から加圧水とを送って噴射ノズ
ル18で噴射するときに水を加えて混合しながら法面1に
所定の厚さに吹付けることによって植生基盤2が形成さ
れる。The above-mentioned vegetation base 2 is formed when the vegetation base material 10 is put into the mortar spraying machine 15 and stirred and mixed, and then compressed air from the compressor 16 and pressurized water from the power sprayer 17 are sent by the spray nozzle 18. The vegetation base 2 is formed by spraying the slope 1 with a predetermined thickness while adding and mixing water to the slope.
そして、当該吹付機15に接続するホース先端の噴射ノズ
ル18によって、第2〜4図の排水処理工の法面1、或い
は、第5〜7図の丸太伏せ工における隣合う丸太の間隔
Hの間における各法面1に所定の厚さ(図示例は5cm)
に吹き付ける。Then, by the injection nozzle 18 at the tip of the hose connected to the spraying machine 15, the slope 1 of the wastewater treatment work shown in FIGS. 2 to 4 or the interval H between adjacent logs in the log felling work shown in FIGS. Specified thickness on each slope 1 in the interval (5 cm in the example shown)
Spray on.
また、植生基盤2の表面に種子付きのネットを張る緑化
ネット工を行うときには、次の如くである。In addition, when performing a greening net work in which a net with seeds is stretched on the surface of the vegetation base 2, it is as follows.
(III)「緑化ネット工の施工例」 ・ネット体(養生材付き) 120m2 (治山用12mm×12mm、20mm×25mm) (一般用12mm×12mm、20mm×25mm) ・種 1.0kg (ケンタッキ‐31-フェスク、クリーンピングレッドフ
ェスク、その他) ・アンカー(メイン) 15本 ・補助アンカー(目串) 300本 上記緑化ネット工の工事にあたっては、第8図のよう
に、ネット体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て製作
し、当該ネット体を、その養生材・種子を下に向けて養
生基盤2の表に密接的に張設する。そして、排水処理工
にあっては、上下の間隔S又は左右に間隔S1をもたせた
排水溝6に沿う近傍の植生基盤2に苗木類9を、又丸太
伏せ工にあっては、アンカー8で固定した丸太7の直上
部位における植生基盤2に苗木類9をそれぞれ植栽す
る。(III) · net body "construction cases of greening net Engineering" (with curing material) 120m 2 (forest conservation for 12mm × 12mm, 20mm × 25mm) ( for general use 12mm × 12mm, 20mm × 25mm) · species 1.0kg (Kentucky - 31-Fescue, cleanping red fescue, others) ・ Anchor (main) 15 pieces ・ Auxiliary anchor (mesh skewer) 300 pieces When constructing the above-mentioned greening net work, as shown in FIG. The curing material 4 made of coarse fiber is laid, and the seeds 5 are entwined so as not to fall off. The net body is closely attached to the surface of the curing base 2 with the curing material and the seeds facing downward. Set up. Then, in the wastewater treatment work, the seedlings 9 are put on the vegetation base 2 in the vicinity along the drainage groove 6 having the vertical space S or the horizontal space S 1 and the anchor 8 in the log felling work. Seedlings 9 are planted on the vegetation base 2 immediately above the log 7 fixed in step 2.
本発明は上記の構成であるから、法面緑化工事における
植生基盤形成方法において、基盤材を形成するのに従来
のように、山砂及びコーティング肥料を使用する代わり
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二次醗酵させて堆肥を作り、これに
水を加えて混合しながら法面に所定厚さの基盤材になる
ように吹付けることによって、従来必ず必要とされてい
た山砂及びコーティング肥料が不要となる。さらに、前
記の植生基盤材は、下水汚泥や生活廃棄物若しくは産業
廃棄物に醗酵菌を混合し、さらに水分調整材を加えて、
水と共にノズル噴射で吹き付けると、それだけで植生基
盤に自然で且つ適度の粘性が生じるから、従来使用して
いたポリ酢酸ビニルやアスファルト乳剤等の化学質粘着
材、又は、前記化学質粘着材に代わる、コンニャクの飛
粉等の純植物性粘着材の使用も不要となり、法面緑化工
事のコストを低減できる効果がある。Since the present invention has the above-mentioned configuration, in the method for forming a vegetation base in slope greening work, organic sewage sludge and other organic sludge instead of using sand and coating fertilizer is conventionally used to form the base material. With respect to the waste, a porous moisture control material having air permeability and sufficient oxygen supply and fermenting bacteria are added to secondary fermentation to make compost, and water is added to this while mixing. By spraying the slope so that the base material has a predetermined thickness, the sand and coating fertilizer, which were always required in the past, can be eliminated. Furthermore, the above-mentioned vegetation base material is a sewage sludge or domestic waste or industrial waste mixed with a fermenting bacterium, and further added with a water conditioner,
If sprayed with water by a nozzle jet, the vegetation base itself will have a natural and appropriate viscosity, so chemical adhesives such as polyvinyl acetate and asphalt emulsions, which have been used conventionally, or the above-mentioned chemical adhesives can be used instead. The use of pure vegetable adhesive such as konjak flying powder is also unnecessary, which has the effect of reducing the cost of slope greening work.
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年以上掛かるが、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って、含水率が均一な堆肥が得ら
れる。In addition, it usually takes 2 years or more to naturally ferment organic living waste / industrial waste, but as in the present invention, a porous water conditioner and a fermenting bacterium are added to the above-mentioned waste in the fermentation machine. By fermenting, compost with a uniform water 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た堆肥には多くの微生物が含ま
れている。従って、自然の客土と殆ど同等な品質が得ら
れる。Furthermore, since the microorganisms in the soil necessary for greening are used in large quantities at the fermentation stage, the compost produced contains many microorganisms. Therefore, the quality is almost the same as the natural soil.
而も、前記の堆肥の形成にあたっては、公共の下水を主
原料とするから、例えば、法面緑化工事における1年間
の山砂使用量9000m3であるとすると、下水汚泥から9000
m3の堆肥を、1m3(700kg)を二次醗酵させて得るために
は、0.25m3(200kg)に縮小する。In addition, since public sewage is used as the main raw material for the formation of the above-mentioned compost, if, for example, the annual sand consumption of slope planting works is 9000 m 3 , the sewage sludge will generate 9000
The compost m 3, in order to get 1 m 3 of (700 kg) was secondary fermentation is reduced to 0.25m 3 (200kg).
そして、1日当たりの生汚泥の使用量は、9000m3÷12ケ
月÷25日=30m3となる。And the amount of raw sludge used per day is 9000 m 3 ÷ 12 months ÷ 25 days = 30 m 3 .
上記の計算から、1日当たり30m3の堆肥を生産するの
に、1m3×30÷0.25m3=120m3(86.4トン)が見込まれ
る。From the above calculation, 1m 3 × 30 ÷ 0.25m 3 = 120m 3 (86.4 tons) is expected to produce 30m 3 compost per day.
また、公共下水2000tonにより生汚泥1トンが産出さ
れ、その下水2000トンは、人間約625人(1人当たり320
/1日)の下水排出量である。2000 tons of public sewage produces 1 ton of raw sludge, and 2000 tons of sewage is about 625 people (320 per person).
/ 1 day) sewage discharge.
そこで、1日当たり30m3の堆肥を生産するのには、120m
3(86.4トン)の生汚泥が必要である。So, to produce 30m 3 of compost per day, 120m
3 (86.4 tons) of raw sludge is required.
この量は172,800トンの下水が必要であり、約54万人分
の下水処理に匹敵する。This amount requires 172,800 tons of sewage, which is equivalent to sewage treatment for about 540,000 people.
この結果から、分かるように公供の下水廃棄物を殆どそ
っくり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
汚泥を有効に処理して、公害につながる廃棄物の除去に
役立たせ、且つその処理をした廃棄物を無駄なく消化す
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。As can be seen from this result, it is clear that almost all the publicly-owned sewage waste can be effectively used for the formation of vegetation bases in slope revegetation work. It is useful as a method for forming a vegetation base in this kind of slope greening work because it can be useful for removing the waste that leads to the above, and the waste that has been treated can be digested without waste.
また、植生基盤にネット体を張設したものにあっては、
その基盤に確実に根活着し、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。而も、排水処理
工における排水溝の近傍その他の位置の植生基盤又は丸
太伏せ工における丸太直上部位若しくはその他の位置の
植生基盤に植えた苗木・草木類は、植生基盤が有する肥
料栄養分によって、別に特別の肥料を施さなくても成育
の促進を助成する効果がある。Also, in the case where the net body is stretched on the vegetation base,
The roots are firmly rooted on the base and covered with a protective material until germination to prevent runoff from rainwater. In addition, seedlings and plants planted on the vegetation base in the vicinity of the drainage ditch in the wastewater treatment works or on the logs directly above the logs in the log felling work or on the vegetation base in other positions are separated according to the fertilizer nutrients of the vegetation base. It has the effect of supporting the promotion of growth without applying special fertilizer.
図は本発明方法の実施例を示すもので、第1図は法面緑
化工事の施工例を示す概略図、第2図〜第4図は排水処
理工を示し、第2図は正面図、第3図は第2図の3−3
線に沿う拡大断面図、第4図は第2図の4−4線に沿う
拡大断面図、第5図〜第7図は丸太伏せ工を示し、第5
図は正面図、第6図は第5図の6−6線に沿う拡大断面
図、第7図は第5図のa部の拡大断面図、第8図は植生
基盤の表面に張設する緑化ネット体の一部の斜視図であ
る。 1……法面 2……植生基盤 3……ネット体 4……養生材 5……種子 6……排水溝 7……丸太 8……アンカー 9……苗木FIG. 1 shows an embodiment of the method of the present invention. FIG. 1 is a schematic view showing a construction example of slope greening work, FIGS. 2 to 4 show wastewater treatment works, and FIG. 2 is a front view. FIG. 3 is 3-3 of FIG.
5 is an enlarged cross-sectional view taken along line 4-4 of FIG. 2, and FIGS.
The figure is a front view, FIG. 6 is an enlarged sectional view taken along line 6-6 of FIG. 5, FIG. 7 is an enlarged sectional view of part a of FIG. 5, and FIG. 8 is stretched on the surface of a vegetation base. It is a perspective view of a part of greening net body. 1 ... Slope 2 ... Vegetation base 3 ... Net body 4 ... Curing material 5 ... Seed 6 ... Drainage groove 7 ... Log 8 ... Anchor 9 ... Sapling
Claims (2)
防ぐための法面排水処理工において、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、
前記醗酵機械によって二次醗酵させて堆肥を作り、その
堆肥をモルタル吹付機を用いてそのノズル噴射時に水を
混合しながら排水処理工法面及び排水溝面に所定厚さに
なるように吹き付けて植生基盤を形成し、前記植生基盤
の表面に、種子及び種子用養生材を備えたネット体を張
り巡らしてアンカーで固定した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。1. A sloped wastewater treatment facility for preventing the collapse slope and the cut slope from being washed away by water, etc., in which organic sewage sludge or domestic waste or industrial waste is put into a fermentation machine, and then perforated. After adding quality moisture regulator and fermentation bacterium,
Secondary fermenting is performed by the fermentation machine to make compost, and the compost is sprayed with a mortar spraying machine while mixing water at the time of its nozzle spraying on the wastewater treatment method surface and drainage groove surface to a predetermined thickness and vegetation. A method for forming a vegetation base in a slope greening construction, comprising forming a base, laying a net body comprising seeds and a seed curing material on the surface of the vegetation base, and fixing the net with an anchor.
めの間伐材利用による丸太伏せ工において、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、前記醗酵機械によって二次醗酵させて堆肥を作り、
その堆肥をモルタル吹付機を用いてそのノズル噴射時に
水を混合しながら丸太伏せ工の隣合う丸太間の法面に所
定厚さになるように吹き付けて植生基盤を形成し、前記
植生基盤の表面に、種子及び種子用養生材を備えたネッ
ト体を張り巡らしてアンカーで固定し、丸太伏せ工にお
ける丸太の直上部位に苗木を植栽したことを特徴とする
法面緑化工事における植生基盤の形成方法。2. An organic sewage sludge or domestic waste or industrial waste is put into a fermentation machine in a log felling process using thinned wood to enhance water retention of a greening base and to ensure safety. After adding the water content adjusting material and the fermentation bacterium, the second fermentation is performed by the fermentation machine to make compost,
Using a mortar spraying machine, the compost is sprayed to a predetermined thickness on the slope between the adjacent logs of the log felling machine while mixing water at the time of spraying the nozzle to form a vegetation base, and the surface of the vegetation base. Forming a vegetation base in the slope reforestation work, which is characterized in that a net body provided with seeds and a curing material for seeds is stretched around and fixed with an anchor, and a seedling is planted immediately above the log in the log felling work. Method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63054292A JPH0723614B2 (en) | 1988-03-08 | 1988-03-08 | Method of forming vegetation base in slope greening work |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63054292A JPH0723614B2 (en) | 1988-03-08 | 1988-03-08 | Method of forming vegetation base in slope greening work |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH01226933A JPH01226933A (en) | 1989-09-11 |
| JPH0723614B2 true JPH0723614B2 (en) | 1995-03-15 |
Family
ID=12966492
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP63054292A Expired - Lifetime JPH0723614B2 (en) | 1988-03-08 | 1988-03-08 | Method of forming vegetation base in slope greening work |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0723614B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0734463A (en) * | 1993-07-17 | 1995-02-03 | Nisshoku Corp | Plantation construction |
| JPH07127067A (en) * | 1993-11-04 | 1995-05-16 | Nisshoku Corp | Planting method for ground cover plant or low shrub using artificial lawn |
Family Cites Families (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS525254U (en) * | 1975-06-27 | 1977-01-14 | ||
| JPS593089A (en) * | 1982-06-29 | 1984-01-09 | 三機工業株式会社 | Manufacture of organic fertilizer |
| JPS621050A (en) * | 1985-02-06 | 1987-01-07 | Hitachi Ltd | Memory check device |
| JPS62182316A (en) * | 1986-02-07 | 1987-08-10 | Jiyoumou Riyokusan Kogyo Kk | Log-laying work for slope protection work by vegetation |
-
1988
- 1988-03-08 JP JP63054292A patent/JPH0723614B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPH01226933A (en) | 1989-09-11 |
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