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JP3935690B2 - Slope greening method - Google Patents
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JP3935690B2 - Slope greening method - Google Patents

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Publication number
JP3935690B2
JP3935690B2 JP2001209142A JP2001209142A JP3935690B2 JP 3935690 B2 JP3935690 B2 JP 3935690B2 JP 2001209142 A JP2001209142 A JP 2001209142A JP 2001209142 A JP2001209142 A JP 2001209142A JP 3935690 B2 JP3935690 B2 JP 3935690B2
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Japan
Prior art keywords
slope
drainage
plate
acidic
vegetation base
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JP2003020652A (en
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英夫 杉本
昭雄 鯉田
隆行 大月
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Obayashi Corp
Landes Co Ltd
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Obayashi Corp
Landes Co Ltd
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Description

【0001】
【発明の属する技術分野】
本発明は、法面保護の目的で盛土等の傾斜地盤を緑化する際の法面緑化方法に関する。
【0002】
【従来の技術】
造成地の盛土や切土、道路の盛土、河川堤防等に見られる傾斜地においては、適当な手段でこれを保護することにより、法面の侵食、剥離、落石等を未然に防止しなければならない。
【0003】
法面保護の手段としては、コンクリートやモルタルの吹付けがその典型的な方法として知られているが、最近では、環境面に配慮すべく、緑化による法面保護を採用することが多くなってきた。
【0004】
法面を緑化によって保護する方法としては、植物の種子、肥料、水、チップ材、粘着剤等を攪拌混合した水性スラリーからなる植生基盤を法面に吹き付けるのが一般的であり、かかる方法によれば、法面への吹付け後、一定期間後に発芽した植物の根が傾斜地盤内に拡がって該傾斜地盤を安定させることが可能となる。
【0005】
【発明が解決しようとする課題】
ここで、植物が生育するためには、その生育に適したpH環境が必要であり、傾斜地盤の表層のpHが小さすぎたり大きすぎたりすると、該傾斜地盤を緑化することは難しくなる。
【0006】
ところが、最近では、土壌が酸性化しているために法面緑化を施しても植樹した樹木が生育せず枯れてしまうことがあるという問題を生じていた。
【0007】
すなわち、かつては海底であった堆積層が地上に隆起している場合、地盤造成時の切土工事で該堆積層が地表に露出することとなるが、かかる堆積層には硫化物が含まれていることが多く、該硫化物が地表への露出によって酸化され、硫酸が発生して法面の表層を酸性化させてしまう。
【0008】
かかる問題は、法面にいったんセメント系材料を吹き付けてから植生基盤を吹き付けたり、法面に排水シートを敷設してから植生基盤を吹き付けたり、植生基盤自体にアルカリ成分を予め含ませておいたりといった方法で回避しようと試みられてはいるが、セメント系材料や排水シートでは、酸性土壌の影響を遮断することはできても、植生基盤で生育する植物の根の伸長を妨げ、ひいては植物の生育に支障をきたすという問題や、植生基盤自体にアルカリ成分を含ませておく方法では、植生基盤のpHが大きくなりすぎて植物の生育を当初から妨げてしまうという問題を引き起こす。
【0009】
本発明は、上述した事情を考慮してなされたもので、法面の土壌が酸性化している場合にも緑化を確実に行うことが可能な法面緑化方法を提供することを目的とする。
【0010】
【課題を解決するための手段】
上記目的を達成するため、本発明に係る法面緑化方法は請求項1に記載したように、所定の排水性中和板を酸性土壌の法面に配置し、しかる後、前記排水性中和板の上に植生基盤を吹き付ける法面緑化方法であって、前記排水性中和板の配置領域の外側に集排水手段を設置するとともに、前記排水性中和板を、多数のチップを該チップ同士に間隙が生じるようにセメント含有物質で相互に固結させて構成することで、前記酸性土壌側の面から浸入した酸性水が中和され、該酸性水が断面内で面内方向に排水され、かつ前記排水性中和板のセメント含有物質が分解されるように構成し、前記配置領域を矩形領域とするとともに、その長手方向が前記法面の傾斜方向に対して該法面上で所定の角度をなす領域とし、前記配置領域の長手方向斜め上縁及び長手方向斜め下縁の各外側に前記集排水手段を設置するものである。
【0014】
また、本発明に係る法面緑化方法は、前記チップを木片で構成したものである。
【0015】
参考発明に係る法面緑化方法にしたがって法面緑化を行うにあたっては、まず、所定の排水性中和板を釘等の固定手段を用いて酸性土壌の法面に固定するとともに固定された前記排水性中和板にメタル系のラス、プラスチック系のネットといった網目体を重ね、該網目体を法面に固定する。
【0016】
次に、排水性中和板の上に植生基盤を吹き付ける。
【0017】
このようにすると、参考発明で用いる排水性中和板を安定した状態にて法面に配置することができるとともに、かかる排水性中和板が、酸性土壌の法面から浸入してきた酸性水を中和するとともに、該酸性水を断面内で面内方向に排水させるように構成してあるため、降雨等が原因で酸性土壌から酸性水が浸出してきたとしても、該酸性水は、植生基盤には直接浸入せず、排水性中和板にまずは浸入する。
【0018】
そして、排水性中和板に浸入した酸性水は、該排水性中和板の中和作用によって中和されるため、その後で植生基盤に浸入したとしても、植生基盤におけるpH環境には何らの悪影響も与えない。むしろ、排水性中和板に浸入した酸性水は、中和された後、その一部が表面張力等によって排水性中和板内に残留し、しかる後、気化や毛細管現象によって植生基盤に浸入して適度な水分を供給する役目を果たすこととなり、植生基盤の乾燥を抑制することが可能となる。
【0019】
また、酸性土壌から排水性中和板に浸入してきた酸性水を中和しきれず、例えば弱酸性にとどまったとしても、該酸性水は、排水性中和板の排水作用によって断面内で面内方向に排水され、植生基盤に浸入することなく、やがて法尻側に達する。そのため、やはり植生基盤における樹木の生育には何らの悪影響も与えない。
【0020】
一方、排水性中和板は、前記酸性水によって分解するように構成してあるため、該排水性中和板は、酸性水を中和しながら徐々に弱アルカリ、中性へと移行し、やがて分解する。
【0021】
したがって、植生基盤で生育する樹木は、分解された排水性中和板を貫通してその下の土壌に根を伸長させ、順調に生育を続ける。なお、植生基盤が吹き付けられた当初、酸性であった土壌は、上述した中和作用によって非酸性環境へと移行しており、この点においても、植生基盤での樹木を適切なpH環境で生育させることができる。
【0022】
請求項1に係る法面緑化方法にしたがって法面緑化を行うにあたっては、まず、所定の排水性中和板を酸性土壌の法面に配置し、該排水性中和板の上に植生基盤を吹き付けるとともに、排水性中和板の配置領域の外側に集排水手段を設置する。
【0023】
このように排水性中和板を酸性土壌の法面に配置した上、該排水性中和板の上に植生基盤を吹き付けると、本発明で用いる排水性中和板が、酸性土壌の法面から浸入してきた酸性水を中和するとともに、該酸性水を断面内で面内方向に排水させるように構成してあるため、降雨等が原因で酸性土壌から酸性水が浸出してきたとしても、該酸性水は、植生基盤には直接浸入せず、排水性中和板にまずは浸入する。
【0024】
そして、排水性中和板に浸入した酸性水は、該排水性中和板の中和作用によって中和されるため、その後で植生基盤に浸入したとしても、植生基盤におけるpH環境には何らの悪影響も与えない。むしろ、排水性中和板に浸入した酸性水は、中和された後、その一部が表面張力等によって排水性中和板内に残留し、しかる後、気化や毛細管現象によって植生基盤に浸入して適度な水分を供給する役目を果たすこととなり、植生基盤の乾燥を抑制することが可能となる。
【0025】
また、酸性土壌から排水性中和板に浸入してきた酸性水を中和しきれず、例えば弱酸性にとどまったとしても、該酸性水は、排水性中和板の排水作用によって断面内で面内方向に排水され、植生基盤に浸入することなく、やがて法尻側に達する。そのため、やはり植生基盤における樹木の生育には何らの悪影響も与えない。
【0026】
一方、排水性中和板は、前記酸性水によって分解するように構成してあるため、該排水性中和板は、酸性水を中和しながら徐々に弱アルカリ、中性へと移行し、やがて分解する。
【0027】
したがって、植生基盤で生育する樹木は、分解された排水性中和板を貫通してその下の土壌に根を伸長させ、順調に生育を続ける。なお、植生基盤が吹き付けられた当初、酸性であった土壌は、上述した中和作用によって非酸性環境へと移行しており、この点においても、植生基盤での樹木を適切なpH環境で生育させることができる。
【0028】
なお、上述した植生基盤の吹付けと集排水手段の配置は、いずれを先行施工するようにしてもかまわない。
【0029】
さらに、請求項1に係る法面緑化方法においては上述したように、排水性中和板の配置領域の外側に集排水手段を設置するようにしたので、降雨等による水を集排水して排水性中和板の配置領域への流入を防止することが可能となり、該配置領域における酸性物質の溶出を抑制することができるとともに、配置領域の法面から浸出してきた酸性水を集排水して該配置領域からの流出を防止することが可能となり、周辺土壌を酸性化する懸念もなくなる。
【0031】
集排水手段をどのように構成するかは任意であり、U字溝、排水パイプ等の公知の手段で適宜構成してもよいし、配置領域の縁部に沿って溝を掘削するとともに該溝に砂利等のドレーン体を充填するように構成してもよい。
【0032】
ここで前記配置領域を矩形領域とするとともに、その長手方向が前記法面の傾斜方向に対して該法面上で所定の角度をなす領域とし、前記配置領域の長手方向斜め上縁及び長手方向斜め下縁の各外側に前記集排水手段を設置する場合においては、配置領域の上方からの水の流入及び下方への酸性水の流出を防止することができる。なお、かかる発明は、法面に露出した地層の方向が鉛直ではなく、所定の角度だけ傾斜していたり水平であったりする場合において、かかる地層が酸性土壌である場合に特に有効な手段となる。
【0033】
上述した各発明で用いる排水性中和板は、多数のチップを該チップ同士に間隙が生じるようにセメント含有物質で相互に固結させて構成する。
【0034】
かかる構成においては、チップ同士の間隙によって排水機能が、セメント含有物質によるアルカリ性によって中和機能がそれぞれ確保されるとともに、セメント含有物質によるチップ同士の固結作用によって板としての強度が確保される。
【0035】
また、セメント含有物質に含まれるセメントが、主として、珪酸、アルミナ、酸化鉄の石灰塩と少量のアルカリ化合物からなるため、酸によって可溶性の石灰塩となり、かくして所定の分解機能を有することとなる。特に、硫酸、塩酸、硝酸のような強い無機酸は、セメント中の水酸化カルシウムを中和するとともに、比較的安定な硬化生成物である石灰の珪酸塩やアルミナ塩まで分解する。また、ナトリウム、マグネシウム、カルシウムの硫酸塩などの塩類は、セメント中の水酸化カルシウムと反応して可溶性の物質を作ったり、多量の結晶水をとって膨張し、セメントを分解する。
【0036】
セメント含有物質とは、具体的には、セメントと水との水和反応によって水酸化カルシウムが生成したものであれば、その形態は任意であり、セメント及び水とからなるセメントミルク(セメントペースト)、セメント、水及び細骨材からなるフレッシュモルタルあるいはセメント、水、細骨材及び粗骨材からなるフレッシュコンクリートのいずれを水和反応で硬化させたものであってもかまわない。
【0037】
上述したチップをどのような材料で構成するかは任意であるが、該チップを木片で構成した場合においては、チップについても微生物による分解作用を受けることとなるため、上述したセメント含有物質の分解作用と相まって排水性中和板は、経年的に確実に分解することとなり、その上に吹き付けられた植生基盤の樹木は、分解された排水性中和板の割れ目や微生物分解で生成した中空空間に根を伸長させ、通常の土壌と同様に生育していく。
【0038】
【発明の実施の形態】
以下、本発明に係る法面緑化方法の実施の形態について、添付図面を参照して説明する。なお、従来技術と実質的に同一の部品等については同一の符号を付してその説明を省略する。
【0039】
図1は、本実施形態に係る法面緑化方法を実施する手順を示したフローチャート、図2は、該法面緑化方法に用いる排水性中和板を示した図である。これらの図でわかるように、本実施形態に係る法面緑化方法においては、まず、排水性中和板1を図3に示すように、固定手段である釘41を用いて酸性土壌11の法面12に固定する(ステップ101)。
【0040】
排水性中和板1は図2(b)でよくわかるように、多数のチップである木片2を該木片同士に間隙3が生じるようにセメント含有物質であるセメントペースト4で相互に固結させてなり、一方の側から浸入してきた酸性水をセメントペースト4に含まれる水酸化カルシウムで中和するとともに、該酸性水を間隙3を介して断面内で面内方向(同図(a)矢印方向)に排水させることができるようになっている。
【0041】
すなわち、排水性中和板1は、木片2をセメント含有物質であるセメントペースト4で相互に固結させてあるため、運搬、配置等においては、板としての所定の強度を有し、施工上、何らの支障も生じないし、木片2同士に間隙3が生じるようにしてあるため、釘41の打込みによって割れが生じる懸念もない。
【0042】
また、排水性中和板1は、セメントペースト4が酸性水によって中和されて強アルカリから弱アルカリあるいは中性へと移行し、それに伴って分解するようになっている。
【0043】
本実施形態に用いる排水性中和板1を製造するには、例えば数cmの大きさの木片2とセメントと少量の水とをミキサー内で混合して木片2の表面にセメントペーストを絡ませるようにし、かかる状態で板状物製作用型枠内に投入し、所要の加圧状態で硬化させて板状に成形した後、適宜乾燥させればよい。
【0044】
ここで、セメントペーストが多すぎると、製造された排水性中和板1内の間隙3が少なくなり、セメントペーストが少なすぎると、木片2同士を固結させる強度が不足して板状体としての強度が不足するため、セメント及び水の量は、かかる観点を考慮して適宜決定する。
【0045】
排水性中和板1を酸性土壌11の法面12に固定するにあたっては、該排水性中和板を配置することによって法面12の緑化を図るのに必要十分な配置領域42を図4(a)に示すように予め定め、該配置領域に合わせて複数の排水性中和板1を配置すればよい。
【0046】
ここで、排水性中和板1が配置される配置領域42は、同図によれば、法面12の勾配に対して傾斜した領域となっているが、これは、酸性土壌、すなわち、酸性物質が溶出される地層が傾斜した状態で地上に露出していることを想定しているためである。
【0047】
なお、配置領域42への配置の仕方については、図4(b)に示すように複数の排水性中和板1を隙間なく配置するようにしてもよいが、配置領域42の形状や幅によっては、配置領域42に合わせて排水性中和板1を現場で切断する必要が生じる場合がある。
【0048】
このような場合には同図(c)に示すように、排水性中和板1を互いに所定の間隔dが形成されるように配置してもよい。かかる構成によれば、配置領域42の形状や幅に応じて排水性中和板1同士の隙間dを適宜調整することにより、排水性中和板1を現場で切断する必要がなくなり、施工の手間を省略することができるとともに、使用されない排水性中和板1の端材が発生するのを防止し、資材の無駄をなくすことが可能となる。
【0049】
なお、いずれにしろ、排水性中和板1が配置される配置領域42を予め定めるにあたっては、緑化したい酸性土壌の分布範囲を把握し、該酸性土壌の分布範囲をすべて覆うことができるように設定するのが望ましい。
【0050】
次に、図5に示すように、排水性中和板1が配置された配置領域42の長手方向斜め上縁及び斜め下縁の各外側に集排水手段としての集排水体44,44を設置する(ステップ102)。
【0051】
集排水体44は、市販されている排水材やドレーン材から適宜選択することが可能であり、例えば、数本の排水パイプを並列させるとともに、該排水パイプを不織布等の透水性シートと所定の遮水シートとで挟み込んで構成したものを用いることができる。かかる集排水体の場合には、遮水シートが上に、透水性シートが法面12に当接するように設置すればよい。
【0052】
また、集排水体44,44は同図に示すように、配置領域42の両縁部に隣接させて設置することが考えられる。
【0053】
次に、引き続き同図に示すように、排水性中和板1に網目体としてのラス43を重ねた上、該ラスを法面12に固定する(ステップ103)。
【0054】
このようにラス43を排水性中和板1に重ねると、釘41の固定作用と相まって排水性中和板1を安定した状態にて法面12に配置することが可能となる。
【0055】
ラス43は例えば、排水性中和板1同士の隙間に、又は排水性中和板1を貫通するようにしてアンカーピンを法面12に打ち込んで固定すればよい。なお、ラス43は、排水性中和板1の配置安定性を高めるのみならず、後述する植生基盤13の吹付けの際、該植生基盤が未だ固まらない状態においてはこれが流下しないように保持するとともに、硬化した状態においてはこれを補強する役目をも果たす。
【0056】
次に、図6に示すように、排水性中和板1の上に植生基盤13を例えば数cmの厚みで吹き付ける(ステップ104)。
【0057】
植生基盤13は、植物の種子、肥料、水、チップ材、粘着剤等を攪拌混合した水性スラリーから構成することが考えられる。
【0058】
このように排水性中和板1を酸性土壌11の法面12に配置してから、該排水性中和板の上に植生基盤13を吹き付けると、図7に示すように降雨等が原因で酸性土壌11から酸性水が浸出してきたとしても、該酸性水は、植生基盤13には直接浸入せず、排水性中和板1にまずは浸入する。
【0059】
そして、排水性中和板1に浸入した酸性水は、該排水性中和板の中和作用によって中和されるため、その後で植生基盤に浸入したとしても(図7破線方向)、植生基盤13におけるpH環境には何らの悪影響も与えない。
【0060】
むしろ、排水性中和板1に浸入した酸性水は、中和された後、その一部が表面張力等によって排水性中和板内に残留し、しかる後、気化や毛細管現象によって植生基盤13に浸入し、該植生基盤に適度な水分を供給する役目を果たすこととなり、植生基盤13の乾燥を抑制することが可能となる。
【0061】
また、酸性土壌11から排水性中和板1に浸入してきた酸性水を中和しきれず、弱酸性にとどまったとしても、該酸性水は、間隙3を介した排水性中和板1の排水作用によって断面内で面内方向に排水され(図7実線方向、図2(a)参照)、植生基盤13に浸入することなく、やがて法尻側に達する。そのため、やはり植生基盤13における樹木の生育には何らの悪影響も与えない。
【0062】
さらに、排水性中和板1の配置領域42の外側に集排水体44,44を設置してあるため、図8に示すように、降雨等による水は、上縁側の集排水体44で集排水され、配置領域42には流入しない。また、配置領域42の法面12から浸出した酸性水の一部が、法面勾配の関係上、排水性中和板1の面内方向に排水されなかったとしても、かかる酸性水は、下縁側の集排水体44で集排水され、配置領域42から流出することはない。
【0063】
一方、排水性中和板1は、酸性土壌11からの酸性水を中和しながら、徐々に弱アルカリ、中性へとpH環境が移行するとともに、それに伴ってセメントペースト4が分解する。そして、かかるセメントペースト4で固結されていた木片2がバラバラになるため、結局、排水性中和板1全体が分解する。
【0064】
また、セメントペースト4の分解によってバラバラになった木片2についても、土中の微生物による分解作用を受けるため、排水性中和板1は、上述したセメントペースト4の分解作用と相まって経年的に確実に分解する。
【0065】
したがって、植生基盤13で生育する樹木31は図9に示すように、分解された排水性中和板1を貫通してその下の土壌11aに根を伸長させ、順調に生育を続ける。なお、植生基盤13が吹き付けられた当初、酸性であった土壌11は、上述した中和作用によって非酸性環境の土壌11aへと移行しており、この点においても、植生基盤13での樹木を適切なpH環境で生育させることができる。
【0066】
なお、排水性中和板1は、ほとんどが木片2であるため、微生物の分解作用を受けた後は、土壌11aと一体化する。
【0067】
以上説明したように、本実施形態に係る法面緑化方法によれば、酸性土壌11側の面から浸入してきた酸性水を排水性中和板1で中和させるとともに、該酸性水を排水性中和板1の断面内で面内方向に排水させることができる。
【0068】
そのため、降雨等が原因で酸性土壌11から酸性水が浸出してきたとしても、該酸性水を排水性中和板1の中和作用によって中和させるとともに、酸性水が中和されずに弱酸性にとどまったとしても、該酸性水を排水性中和板1の排水作用によって断面内で面内方向に排水させることが可能となり、植生基盤13を酸性土壌11から遮断する、言い換えれば、酸性水が植生基盤13に浸入するのを未然に防止することが可能となる。
【0069】
一方、排水性中和板1を酸性水によって分解するように構成してあるため、該排水性中和板は、酸性水を中和しながら徐々に中性環境へと移行し、やがて上述したように分解し、植生基盤13で生育する樹木31は、かかる分解された排水性中和板1の割れ目や分解によって生じた空隙を利用しながら、中性の環境となった土壌11a内へとその根を伸長させる。
【0070】
したがって、植生基盤13で生育する樹木31を、適切なpH環境に維持しつつ、なおかつその根を土壌11aに伸長させながら順調に生育させることが可能となり、かくして酸性土壌11であっても緑化を行うことが可能となる。
【0071】
また、本実施形態に係る法面緑化方法によれば、排水性中和板1を釘41を用いて酸性土壌11の法面12に固定するとともに、固定された排水性中和板1にラス43を重ねた上、該ラスを法面12に固定するようにしたので、排水性中和板1が釘41とラス43の両方で二重に固定されることとなり、かくして該排水性中和板を安定した状態にて法面12上に配置することが可能となる。
【0072】
したがって、特に我が国では、土地の有効活用の観点から急勾配な法面が切土工事で出現することが多いが、本実施形態に係る法面緑化方法によれば、酸性土壌11の法面12が急勾配であっても、排水性中和板1が滑落するおそれがないため、わざわざ法尻から順に積み上げていかずとも、緑化を施したい配置領域42だけに排水性中和板1を配置すれば足りることとなり、酸性土壌11が急勾配であっても確実に緑化することが可能となるのみならず、その際に必要となる排水性中和板1の数を必要最小限にとどめることが可能となり、経済性にも優れた緑化方法となる。
【0073】
また、本実施形態に係る法面緑化方法によれば、排水性中和板1の配置領域42の外側のうち、上縁及び下縁側に集排水体44,44を設置したので、降雨等による水の配置領域42への流入を防止することが可能となり、該配置領域における酸性物質の溶出を抑制することができるとともに、配置領域42の法面12から浸出してきた酸性水を集排水して該配置領域からの流出を防止することが可能となり、周辺土壌を酸性化する懸念もなくなる。
【0074】
また、本実施形態に係る法面緑化方法によれば、チップを木片2で構成したので、該木片が微生物によって分解されることとなり、上述したセメントの分解作用と相まって、排水性中和板1を経年的に確実に分解させることが可能となる。なお、チップを木片2とすることにより、排水性中和板1を軽量化できるという作用効果も奏する。
【0075】
本実施形態では、チップとして木片2を利用したが、樹木の根を伸長させるのに酸によるセメントの分解作用で十分であれば、あえて木片2を用いる必要はなく、互いに空隙を形成させることができるチップであれば、いかなる材料でもよい。例えば、適当な粒径にクラッシャーで粒度調整されたコンクリートガラを用いることも可能である。
【0076】
また、本実施形態では特に言及しなかったが、排水性中和板1を図4(c)に示す配置とした場合、吹き付けられた植生基盤13がラス43の網目から排水性中和板1同士の隙間dに多少入り込み、かかる状態で硬化するため、上述した釘41やラス43の固定作用と相まって、排水性中和板1、法面12及び植生基盤13が一体化することとなり、法面が急勾配であっても、排水性中和板1の配置安定性をさらに向上させることが可能となる。
【0077】
但し、かかる配置の仕方を採用する場合については、植生基盤13がラス43の網目を通過して排水性中和板1の隙間dに充填されてしまうことがないよう、排水性中和板1,1間の間隙dや、ラス43の網目の大きさを適宜設定する。このようにすれば、排水性中和板1の隙間dに充填された植生基盤13に法面12からの酸性水が直接浸入して該植生基盤での樹木の成長が阻害されるといった事態を未然に回避することができるとともに、隙間dはそのまま空隙として残るため、酸性水の排水を促進することができるという効果も奏する。
【0078】
また、本実施形態では特に言及しなかったが、緑化の対象となる酸性土壌の法面勾配が緩勾配であるために、排水性中和板を固定手段を用いて法面に固定したり、さらにその上から網目体を重ねて該網目体を法面に固定したりする必要がない場合には、これらの工程を省略してもよい。
【0079】
また、酸性土壌となっている地層がほぼ鉛直であるために、配置領域への雨水の流入や配置領域からの酸性水の流出の懸念がないのであれば、集排水体44,44を設置する工程を省略してもよい。
【0080】
また、本実施形態では特に言及しなかったが、セメントペーストだけでは強度不足のため、木片4を互いに固結させることができないのであれば、適宜、固化剤を添加するようにしてもかまわないし、流動性等の面で改善する必要があるのであれば、適宜、混和剤を使用すればよい。
【0081】
また、本発明のセメント含有物質は、セメントペーストに限るものではなく、細骨材を入れたモルタルを使用する場合も考えられる。
【0082】
【発明の効果】
以上述べたように、本発明に係る法面緑化方法によれば、植生基盤で生育する樹木を、適切なpH環境に維持しつつ、なおかつその根を土壌に伸長させながら順調に生育させることが可能となり、かくして酸性土壌であっても緑化を行うことが可能となる。
【0083】
【図面の簡単な説明】
【図1】本実施形態に係る法面緑化方法の実施手順を示したフローチャート。
【図2】本実施形態に係る法面緑化方法に用いる排水性中和板の図であり、(a)は斜視図、(b)は断面詳細図。
【図3】本実施形態に係る法面緑化方法を実施する手順を示した図。
【図4】引き続き本実施形態に係る法面緑化方法を実施する手順を示した図。
【図5】引き続き本実施形態に係る法面緑化方法を実施する手順を示した図。
【図6】引き続き本実施形態に係る法面緑化方法を実施する手順を示した図。
【図7】本実施形態に係る法面緑化方法の作用を示した図。
【図8】同じく本実施形態に係る法面緑化方法の作用を示した図。
【図9】同じく本実施形態に係る法面緑化方法の作用を示した図。
【符号の説明】
1 排水性中和板
2 木片(チップ)
3 間隙
4 セメントペースト(セメント含有物質)
11 酸性土壌
12 法面
13 植生基盤
41 釘(固定手段)
42 配置領域
43 ラス(網目体)
44 集排水体(集排水手段)
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a slope greening method for greening sloped ground such as embankments for the purpose of slope protection.
[0002]
[Prior art]
On slopes found in embankments and cuts, road embankments, river embankments, etc., it is necessary to prevent slope erosion, delamination, and falling rocks by protecting them with appropriate means. .
[0003]
As a method of slope protection, spraying concrete or mortar is known as a typical method, but recently, in order to consider the environment, slope protection by greening has been increasingly adopted. It was.
[0004]
As a method of protecting the slope by greening, it is common to spray a vegetation base made of an aqueous slurry obtained by stirring and mixing plant seeds, fertilizer, water, chip material, adhesive, etc. on the slope. According to this, after spraying on the slope, the root of the plant that germinates after a certain period of time spreads in the inclined ground, and the inclined ground can be stabilized.
[0005]
[Problems to be solved by the invention]
Here, in order for a plant to grow, a pH environment suitable for its growth is necessary. If the pH of the surface layer of the inclined ground is too small or too large, it becomes difficult to green the inclined ground.
[0006]
However, recently, the soil has been acidified, so that even if the slope is greened, the planted tree does not grow and sometimes dies.
[0007]
In other words, when a sedimentary layer that used to be the seabed is raised above the ground, the sedimentary layer will be exposed to the ground by cutting work during ground preparation, but such a sedimentary layer contains sulfide. In many cases, the sulfide is oxidized by exposure to the surface of the earth, and sulfuric acid is generated to acidify the surface layer of the slope.
[0008]
Such problems include spraying cement material on the slope and then spraying the vegetation base, laying a drainage sheet on the slope and then spraying the vegetation base, or pre-containing the vegetation base itself with an alkaline component. Attempts have been made to avoid this, but cement-based materials and drainage sheets can block the effects of acidic soil, but prevent the growth of plant roots that grow on the vegetation base. The problem of hindering the growth and the method of adding an alkaline component to the vegetation base itself cause a problem that the pH of the vegetation base becomes too high and hinders the growth of the plant from the beginning.
[0009]
The present invention has been made in consideration of the above-described circumstances, and an object of the present invention is to provide a slope revegetation method that can reliably perform revegetation even when the sloped soil is acidified.
[0010]
[Means for Solving the Problems]
In order to achieve the above-mentioned object, the slope revegetation method according to the present invention includes a predetermined drainage neutralization plate placed on a slope of acidic soil as described in claim 1 and then the drainage neutralization. A slope planting method in which a vegetation base is sprayed on a board, and a drainage means is installed outside the area where the drainage neutralization board is disposed, and the drainage neutralization board is provided with a number of chips. By constructing by cementing together with cement-containing materials so that a gap is formed between them, the acid water that has entered from the surface of the acid soil side is neutralized, and the acid water is drained in the in-plane direction within the cross section. And the drainage neutralization plate is configured such that the cement-containing substance is decomposed, and the arrangement region is a rectangular region, and the longitudinal direction of the drainage neutralization plate is on the slope with respect to the slope direction of the slope. A region that forms a predetermined angle, diagonally above the arrangement region in the longitudinal direction And it is intended to install the current draining means to each outer side of the longitudinal oblique lower edge.
[0014]
In the slope greening method according to the present invention, the chip is made of a piece of wood.
[0015]
When performing slope planting according to the slope planting method according to the reference invention, first, the predetermined drainage neutralization plate is fixed to the slope of acidic soil using a fixing means such as a nail and the drainage is fixed. A mesh body such as a metal lath or a plastic net is stacked on the neutral neutralizing plate, and the mesh body is fixed to the slope.
[0016]
Next, the vegetation base is sprayed on the drainage neutralizing plate.
[0017]
In this way, the drainage neutralization plate used in the reference invention can be placed on the slope in a stable state, and the drainage neutralization plate can remove the acidic water that has infiltrated from the slope of the acidic soil. Since it is configured to neutralize and drain the acidic water in the in-plane direction within the cross section, even if acidic water is leached from acidic soil due to rainfall or the like, the acidic water is First of all, do not enter directly into the drainage neutralization plate.
[0018]
The acidic water that has entered the drainage neutralization plate is neutralized by the neutralization action of the drainage neutralization plate, so even if it subsequently enters the vegetation platform, there is no effect on the pH environment in the vegetation platform. There is no adverse effect. Rather, acid water that has entered the drainage neutralization plate is neutralized and part of it remains in the drainage neutralization plate due to surface tension, etc., and then enters the vegetation base by vaporization and capillary action. Thus, it plays a role of supplying appropriate moisture, and it becomes possible to suppress drying of the vegetation base.
[0019]
Moreover, even if the acidic water that has entered the drainable neutralizing plate from the acidic soil cannot be completely neutralized, for example, it remains weakly acidic, the acidic water is in-plane within the cross section due to the draining action of the drainable neutralizing plate. It drains in the direction, and eventually reaches the Houshiri side without entering the vegetation base. Therefore, it does not have any adverse effect on the growth of trees on the vegetation base.
[0020]
On the other hand, since the drainage neutralization plate is configured to be decomposed by the acidic water, the drainage neutralization plate gradually shifts to weak alkali and neutral while neutralizing the acidic water, Decomposes over time.
[0021]
Therefore, trees that grow on the vegetation base penetrate the decomposed drainage neutralization plate, extend the roots to the underlying soil, and continue to grow smoothly. In addition, the soil that was acidic when the vegetation base was sprayed has shifted to a non-acidic environment due to the neutralization action described above, and in this respect as well, the trees on the vegetation base are grown in an appropriate pH environment. Can be made.
[0022]
In performing the revegetation according to the revegetation method according to claim 1, first, a predetermined drainage neutralization board is arranged on the slope of the acidic soil, and a vegetation base is placed on the drainage neutralization board. In addition to spraying, a drainage means is installed outside the area where the drainable neutralizing plate is disposed.
[0023]
As described above, when the drainage neutralization plate is arranged on the slope of the acidic soil, and the vegetation base is sprayed on the drainage neutralization plate, the drainage neutralization plate used in the present invention becomes the slope of the acid soil. Since it is configured to neutralize the acid water that has infiltrated from and drain the acid water in the in-plane direction within the cross section, even if acid water has leached from the acid soil due to rainfall, The acidic water does not directly enter the vegetation base, but first enters the drainage neutralization plate.
[0024]
The acidic water that has entered the drainage neutralization plate is neutralized by the neutralization action of the drainage neutralization plate, so even if it subsequently enters the vegetation platform, there is no effect on the pH environment in the vegetation platform. There is no adverse effect. Rather, acid water that has entered the drainage neutralization plate is neutralized and part of it remains in the drainage neutralization plate due to surface tension, etc., and then enters the vegetation base by vaporization and capillary action. Thus, it plays a role of supplying appropriate moisture, and it becomes possible to suppress drying of the vegetation base.
[0025]
Moreover, even if the acidic water that has entered the drainable neutralizing plate from the acidic soil cannot be completely neutralized, for example, it remains weakly acidic, the acidic water is in-plane within the cross section due to the draining action of the drainable neutralizing plate. It drains in the direction, and eventually reaches the Houshiri side without entering the vegetation base. Therefore, it does not have any adverse effect on the growth of trees on the vegetation base.
[0026]
On the other hand, since the drainage neutralization plate is configured to be decomposed by the acidic water, the drainage neutralization plate gradually shifts to weak alkali and neutral while neutralizing the acidic water, Decomposes over time.
[0027]
Therefore, trees that grow on the vegetation base penetrate the decomposed drainage neutralization plate, extend the roots to the underlying soil, and continue to grow smoothly. In addition, the soil that was acidic when the vegetation base was sprayed has shifted to a non-acidic environment due to the neutralization action described above, and in this respect as well, the trees on the vegetation base are grown in an appropriate pH environment. Can be made.
[0028]
Any of the above-described spraying of the vegetation base and the arrangement of the drainage and drainage means may be performed in advance.
[0029]
Furthermore, in the slope revegetation method according to claim 1, as described above, since the drainage means is installed outside the area where the drainage neutralizing plate is disposed, the water is collected and drained by rain or the like. It is possible to prevent the inflow of the neutralizing plate into the arrangement area, to suppress the elution of acidic substances in the arrangement area, and to collect and drain the acidic water that has leached from the slope of the arrangement area. It becomes possible to prevent the outflow from the arrangement area, and there is no concern of acidifying the surrounding soil.
[0031]
How the drainage means is configured is arbitrary, and may be appropriately configured by a known means such as a U-shaped groove and a drainage pipe, and the groove is excavated along the edge of the arrangement region and the groove. It may be configured to be filled with a drain body such as gravel.
[0032]
Here, the arrangement area is a rectangular area, and the longitudinal direction thereof is an area that forms a predetermined angle on the slope with respect to the slope direction of the slope, and the oblique upper edge and the longitudinal direction of the arrangement area In the case where the drainage means is installed on each outer side of the oblique lower edge, it is possible to prevent the inflow of water from above the arrangement area and the outflow of acidic water to the bottom. Such an invention is a particularly effective means in the case where the direction of the formation exposed on the slope is not vertical but is inclined by a predetermined angle or is horizontal and the formation is acidic soil. .
[0033]
The drainage neutralization plate used in each of the inventions described above is configured by solidifying a large number of chips with a cement-containing substance so that gaps are generated between the chips.
[0034]
In such a configuration, the drainage function is ensured by the gap between the chips, and the neutralization function is secured by the alkalinity of the cement-containing substance, and the strength as a plate is secured by the caking action of the chips by the cement-containing substance.
[0035]
Further, since the cement contained in the cement-containing material is mainly composed of a lime salt of silicic acid, alumina, iron oxide and a small amount of an alkali compound, it becomes a soluble lime salt by an acid and thus has a predetermined decomposition function. In particular, strong inorganic acids such as sulfuric acid, hydrochloric acid, and nitric acid neutralize calcium hydroxide in cement, and decompose to lime silicates and alumina salts, which are relatively stable cured products. In addition, salts such as sodium, magnesium and calcium sulfates react with calcium hydroxide in the cement to form a soluble substance, or swell by taking a large amount of crystal water to decompose the cement.
[0036]
Specifically, the cement-containing substance may have any form as long as calcium hydroxide is generated by a hydration reaction between cement and water, and cement milk (cement paste) composed of cement and water. Any of fresh mortar made of cement, water and fine aggregate or fresh concrete made of cement, water, fine aggregate and coarse aggregate may be cured by a hydration reaction.
[0037]
It is arbitrary what kind of material the chip is made of, but when the chip is made of wood chips, the chip is also subjected to the action of decomposition by microorganisms. Combined with the action, the drainage neutralization plate will surely decompose over time, and the vegetation-based trees sprayed on it will be cracked in the decomposed drainage neutralization plate and hollow spaces generated by microbial decomposition Elongate roots and grow like normal soil.
[0038]
DETAILED DESCRIPTION OF THE INVENTION
DESCRIPTION OF EMBODIMENTS Hereinafter, embodiments of a slope greening method according to the present invention will be described with reference to the accompanying drawings. Note that components that are substantially the same as those of the prior art are assigned the same reference numerals, and descriptions thereof are omitted.
[0039]
FIG. 1 is a flowchart showing a procedure for carrying out the slope greening method according to the present embodiment, and FIG. 2 is a view showing a drainage neutralization plate used in the slope greening method. As can be seen from these figures, in the slope revegetation method according to the present embodiment, first, as shown in FIG. It fixes to the surface 12 (step 101).
[0040]
As shown in FIG. 2 (b), the drainage neutralizing plate 1 is made by solidifying wood chips 2 which are a large number of chips with cement paste 4 which is a cement-containing material so that gaps 3 are formed between the wood pieces. The acidic water that has entered from one side is neutralized with calcium hydroxide contained in the cement paste 4, and the acidic water is passed through the gap 3 in the in-plane direction (arrow (a) in the figure). Direction) can be drained.
[0041]
In other words, the drainable neutralizing plate 1 has wooden pieces 2 solidified together with cement paste 4 which is a cement-containing substance, and therefore has a predetermined strength as a plate in transportation, arrangement, etc. No trouble is caused, and since the gap 3 is formed between the pieces of wood 2, there is no fear of cracking due to the driving of the nail 41.
[0042]
Further, the drainable neutralizing plate 1 is configured such that the cement paste 4 is neutralized with acidic water and is transferred from a strong alkali to a weak alkali or neutral, and is decomposed accordingly.
[0043]
In order to manufacture the drainable neutralizing plate 1 used in the present embodiment, for example, a piece of wood 2 having a size of several centimeters, cement, and a small amount of water are mixed in a mixer and the cement paste is entangled on the surface of the piece of wood 2. In such a state, it is put into a plate-like product working form, cured in a required pressure state and formed into a plate shape, and then dried appropriately.
[0044]
Here, if there is too much cement paste, the gap 3 in the produced drainable neutralizing plate 1 will be reduced, and if there is too little cement paste, the strength for consolidating the pieces of wood 2 will be insufficient and the plate-like body will be formed. In view of this viewpoint, the amount of cement and water is appropriately determined.
[0045]
When fixing the drainage neutralization board 1 to the slope 12 of the acidic soil 11, the placement area 42 necessary and sufficient to plan greening of the slope 12 by placing the drainage neutralization board is shown in FIG. As shown in a), a plurality of drainage neutralizing plates 1 may be arranged in advance according to the arrangement area.
[0046]
Here, according to the figure, the arrangement | positioning area | region 42 where the drainage neutralization board 1 is arrange | positioned becomes an area | region inclined with respect to the slope of the slope 12, but this is acidic soil, ie, acidic This is because it is assumed that the strata from which the material is eluted are exposed to the ground in an inclined state.
[0047]
In addition, about the method of arrangement | positioning to the arrangement | positioning area | region 42, as shown in FIG.4 (b), you may make it arrange | position the some drainage neutralization board 1 without a gap, but it depends on the shape and width of the arrangement | positioning area | region 42. In some cases, it may be necessary to cut the drainable neutralizing plate 1 on site in accordance with the arrangement region 42.
[0048]
In such a case, the drainage neutralizing plates 1 may be arranged so that a predetermined distance d is formed between them as shown in FIG. According to such a configuration, by appropriately adjusting the gap d between the drainage neutralization plates 1 according to the shape and width of the arrangement region 42, it is not necessary to cut the drainage neutralization plate 1 on site, In addition to being able to save labor, it is possible to prevent the end material of the drainage neutralizing plate 1 that is not used from being generated, and to eliminate waste of materials.
[0049]
In any case, in predetermining the arrangement region 42 where the drainage neutralization plate 1 is arranged, the distribution range of the acidic soil to be greened is grasped, and the entire distribution range of the acidic soil can be covered. It is desirable to set.
[0050]
Next, as shown in FIG. 5, drainage bodies 44 and 44 as drainage and drainage means are installed on the outer sides of the diagonally upper edge and the diagonally lower edge in the longitudinal direction of the arrangement region 42 where the drainage neutralizing plate 1 is arranged. (Step 102).
[0051]
The drainage body 44 can be appropriately selected from commercially available drainage materials and drain materials. For example, several drainage pipes are arranged in parallel, and the drainage pipes are laid with a water permeable sheet such as a nonwoven fabric and a predetermined one. What was comprised between the water impervious sheets can be used. In the case of such a drainage body, the water-impervious sheet may be placed on the top and the water-permeable sheet in contact with the slope 12.
[0052]
Further, as shown in the figure, the drainage bodies 44 and 44 may be installed adjacent to both edges of the arrangement region 42.
[0053]
Next, as shown in the figure, a lath 43 as a mesh body is overlaid on the drainable neutralizing plate 1 and the lath is fixed to the slope 12 (step 103).
[0054]
When the lath 43 is overlaid on the drainage neutralization plate 1 in this way, it becomes possible to arrange the drainage neutralization plate 1 on the slope 12 in a stable state in combination with the fixing action of the nail 41.
[0055]
For example, the lath 43 may be fixed by driving an anchor pin into the slope 12 so as to penetrate between the drainage neutralization plates 1 or through the drainage neutralization plate 1. The lath 43 not only enhances the placement stability of the drainage neutralization plate 1 but also holds the vegetation base 13 so that it does not flow down when the vegetation base 13 is sprayed as will be described later. At the same time, it also serves to reinforce this in the cured state.
[0056]
Next, as shown in FIG. 6, the vegetation base 13 is sprayed on the drainable neutralizing plate 1 with a thickness of, for example, several centimeters (step 104).
[0057]
The vegetation base 13 may be composed of an aqueous slurry obtained by stirring and mixing plant seeds, fertilizer, water, a chip material, an adhesive, and the like.
[0058]
Thus, when the drainage neutralization board 1 is arranged on the slope 12 of the acidic soil 11 and then the vegetation base 13 is sprayed on the drainage neutralization board, due to rainfall or the like as shown in FIG. Even if acidic water has leached from the acidic soil 11, the acidic water does not directly enter the vegetation base 13, but first enters the drainage neutralization plate 1.
[0059]
And since the acidic water which permeated the drainage neutralization board 1 is neutralized by the neutralization effect | action of this drainage neutralization board, even if it penetrate | invades into a vegetation base after that (FIG. 7 broken line direction), a vegetation base The pH environment at 13 has no adverse effect.
[0060]
Rather, the acid water that has entered the drainage neutralization plate 1 is neutralized, and a part of the acid water remains in the drainage neutralization plate due to surface tension or the like. Intrusion into the vegetation base and the role of supplying appropriate moisture to the vegetation base, it is possible to suppress the drying of the vegetation base 13.
[0061]
Further, even if the acidic water that has entered the drainable neutralizing plate 1 from the acidic soil 11 cannot be completely neutralized and remains weakly acidic, the acidic water is discharged from the drainable neutralizing plate 1 through the gap 3. The action drains in the in-plane direction within the cross section (see the solid line direction in FIG. 7, see FIG. 2 (a)), and eventually reaches the buttock side without entering the vegetation base 13. Therefore, there is no adverse effect on the growth of trees on the vegetation base 13.
[0062]
Furthermore, since the drainage bodies 44 and 44 are installed outside the arrangement area 42 of the drainage neutralizing plate 1, water due to rain or the like is collected by the drainage body 44 on the upper edge side as shown in FIG. It is drained and does not flow into the arrangement area 42. Even if some of the acidic water leached from the slope 12 of the arrangement region 42 is not drained in the in-plane direction of the drainage neutralization plate 1 due to the slope of the slope, the acidic water is The water is collected and drained by the edge side drainage body 44 and does not flow out of the arrangement area 42.
[0063]
On the other hand, while the neutral environment plate 1 neutralizes the acidic water from the acidic soil 11, the pH environment gradually shifts to weak alkali and neutral, and the cement paste 4 decomposes accordingly. And since the piece 2 of wood solidified with this cement paste 4 falls apart, the drainage neutralization board 1 whole decomposes | disassembles eventually.
[0064]
In addition, the piece of wood 2 that has been disassembled due to the decomposition of the cement paste 4 is also subjected to a decomposition action by microorganisms in the soil, so that the drainable neutralizing plate 1 is reliable over time in combination with the decomposition action of the cement paste 4 described above. Disassembled into
[0065]
Therefore, as shown in FIG. 9, the tree 31 that grows on the vegetation base 13 penetrates the decomposed drainable neutralizing plate 1 and extends the root to the underlying soil 11a, and continues to grow smoothly. In addition, the soil 11 which was acidic at the time of the vegetation base 13 being sprayed has moved to the non-acidic environment soil 11a by the neutralization action described above. It can be grown in a suitable pH environment.
[0066]
In addition, since the drainage neutralization board 1 is mostly the piece of wood 2, after receiving the decomposition | disassembly effect | action of microorganisms, it integrates with the soil 11a.
[0067]
As described above, according to the slope revegetation method according to the present embodiment, the acid water that has entered from the surface on the acidic soil 11 side is neutralized by the drainage neutralization plate 1 and the acid water is drained. Within the cross section of the neutralizing plate 1, it can be drained in the in-plane direction.
[0068]
Therefore, even if acidic water has leached from the acidic soil 11 due to rainfall or the like, the acidic water is neutralized by the neutralizing action of the drainable neutralizing plate 1 and the acidic water is not neutralized but is weakly acidic. However, the acidic water can be drained in the in-plane direction within the cross section by the drainage action of the drainable neutralizing plate 1, and the vegetation base 13 is blocked from the acidic soil 11, in other words, the acidic water Can be prevented from entering the vegetation base 13 beforehand.
[0069]
On the other hand, since the drainable neutralizing plate 1 is configured to be decomposed by acidic water, the drainable neutralizing plate gradually shifts to a neutral environment while neutralizing the acidic water. Thus, the tree 31 that is decomposed and grows on the vegetation base 13 enters the soil 11a that has become a neutral environment while utilizing the cracks of the decomposed drainable neutralizing plate 1 and the voids generated by the decomposition. Elongate its roots.
[0070]
Therefore, it becomes possible to grow the tree 31 growing on the vegetation base 13 smoothly while maintaining the appropriate pH environment and extending the root of the tree 11 to the soil 11a. Can be done.
[0071]
Further, according to the slope greening method according to the present embodiment, the drainage neutralization plate 1 is fixed to the slope 12 of the acidic soil 11 using the nail 41, and the fixed drainage neutralization plate 1 is lathed. 43, and the lath is fixed to the slope 12, so that the drainage neutralizing plate 1 is double-fixed by both the nail 41 and the lath 43, and thus the drainage neutralization is performed. It is possible to arrange the plate on the slope 12 in a stable state.
[0072]
Therefore, especially in Japan, steep slopes often appear in cut work from the viewpoint of effective use of land, but according to the slope revegetation method according to this embodiment, slopes 12 of acidic soil 11 are obtained. Even if the slope is steep, the drainage neutralization plate 1 is not likely to slide down. Therefore, even if the drainage neutralization plate 1 is not stacked in order from the bottom of the method, the drainage neutralization plate 1 should be placed only in the placement area 42 where greening is desired. Therefore, not only can the green soil be surely green even if the acidic soil 11 has a steep slope, but the number of drainage neutralization plates 1 required at that time can be minimized. It becomes possible and it becomes a greening method with excellent economic efficiency.
[0073]
Moreover, according to the slope greening method which concerns on this embodiment, since the drainage body 44,44 was installed in the upper edge and the lower edge side among the arrangement | positioning area | regions 42 of the drainage neutralization board 1, it is due to rain etc. It is possible to prevent water from flowing into the arrangement area 42, to suppress the elution of acidic substances in the arrangement area, and to collect and drain acidic water that has leached from the slope 12 of the arrangement area 42. It becomes possible to prevent the outflow from the arrangement area, and there is no concern of acidifying the surrounding soil.
[0074]
Moreover, according to the slope greening method which concerns on this embodiment, since the chip | tip was comprised with the wood piece 2, this wood piece will be decomposed | disassembled by microorganisms and combined with the decomposition | disassembly effect | action of the cement mentioned above, the drainage neutralization board 1 Can be reliably decomposed over time. In addition, there exists an effect that the drainage neutralization board 1 can be reduced in weight by making the chip | tip into the piece of wood 2. FIG.
[0075]
In this embodiment, the wood piece 2 is used as a chip. However, if the decomposition action of the cement by acid is sufficient to extend the root of the tree, it is not necessary to use the wood piece 2 and gaps can be formed. Any material can be used as long as it is a chip. For example, it is also possible to use concrete glass whose particle size is adjusted with a crusher to an appropriate particle size.
[0076]
Although not particularly mentioned in the present embodiment, when the drainage neutralization plate 1 is arranged as shown in FIG. 4C, the sprayed vegetation base 13 is discharged from the mesh of the lath 43 to the drainage neutralization plate 1. Since it penetrates into the gap d between each other and hardens in such a state, the drainage neutralizing plate 1, the slope 12 and the vegetation base 13 are integrated together with the fixing action of the nails 41 and laths 43 described above. Even if the surface is steep, the placement stability of the drainable neutralizing plate 1 can be further improved.
[0077]
However, in the case of adopting such an arrangement method, the drainage neutralization plate 1 is prevented so that the vegetation base 13 does not pass through the mesh of the lath 43 and fill the gap d of the drainage neutralization plate 1. , 1 and the mesh size of the lath 43 are appropriately set. In this way, the situation is such that the acidic water from the slope 12 directly enters the vegetation base 13 filled in the gap d of the drainage neutralization plate 1 and the growth of trees on the vegetation base is inhibited. In addition to being able to avoid it, the gap d remains as a gap, so that the drainage of acidic water can be promoted.
[0078]
Although not particularly mentioned in the present embodiment, because the slope of the slope of the acid soil to be greened is a gentle slope, the drainage neutralization plate is fixed to the slope using a fixing means, Furthermore, when it is not necessary to overlap the mesh body from above and fix the mesh body to the slope, these steps may be omitted.
[0079]
In addition, since the stratum that is acidic soil is almost vertical, if there is no concern about the inflow of rainwater to the arrangement area or the outflow of acidic water from the arrangement area, the drainage bodies 44, 44 are installed. The process may be omitted.
[0080]
Further, although not particularly mentioned in the present embodiment, if the cement pieces alone are insufficient in strength, and the pieces of wood 4 cannot be consolidated together, a solidifying agent may be appropriately added. If it is necessary to improve in terms of fluidity, an admixture may be used as appropriate.
[0081]
In addition, the cement-containing substance of the present invention is not limited to cement paste, and a mortar containing fine aggregate may be used.
[0082]
【The invention's effect】
As described above, according to the slope revegetation method according to the present invention, it is possible to grow a tree growing on a vegetation base smoothly while maintaining an appropriate pH environment and extending its roots in soil. Thus, greening can be performed even in acidic soil.
[0083]
[Brief description of the drawings]
FIG. 1 is a flowchart showing an implementation procedure of a slope greening method according to the present embodiment.
FIGS. 2A and 2B are views of a drainage neutralization plate used in the slope greening method according to the present embodiment, in which FIG. 2A is a perspective view, and FIG.
FIG. 3 is a diagram showing a procedure for performing a slope greening method according to the present embodiment.
FIG. 4 is a diagram showing a procedure for continuously implementing the slope greening method according to the present embodiment.
FIG. 5 is a view showing a procedure for continuously implementing the slope greening method according to the present embodiment.
FIG. 6 is a diagram showing a procedure for continuously implementing the slope greening method according to the present embodiment.
FIG. 7 is a view showing the operation of the slope greening method according to the present embodiment.
FIG. 8 is a view showing the operation of the slope greening method according to the present embodiment.
FIG. 9 is a view showing the operation of the slope greening method according to the present embodiment.
[Explanation of symbols]
1 Drainage neutralization plate
2 Wood chips (chips)
3 gap
4 Cement paste (cement-containing material)
11 Acid soil
12 Slope
13 Vegetation base
41 Nails (fixing means)
42 Placement area
43 Lath (mesh)
44 Drainage body (collection and drainage means)

Claims (2)

所定の排水性中和板を酸性土壌の法面に配置し、しかる後、前記排水性中和板の上に植生基盤を吹き付ける法面緑化方法であって、前記排水性中和板の配置領域の外側に集排水手段を設置するとともに、前記排水性中和板を、多数のチップを該チップ同士に間隙が生じるようにセメント含有物質で相互に固結させて構成することで、前記酸性土壌側の面から浸入した酸性水が中和され、該酸性水が断面内で面内方向に排水され、かつ前記排水性中和板のセメント含有物質が分解されるように構成し、
前記配置領域を矩形領域とするとともに、その長手方向が前記法面の傾斜方向に対して該法面上で所定の角度をなす領域とし、前記配置領域の長手方向斜め上縁及び長手方向斜め下縁の各外側に前記集排水手段を設置することを特徴とする法面緑化方法。
A predetermined drainage neutralization plate is placed on a slope of acidic soil, and then a vegetation base is sprayed on the drainage neutralization plate, where the drainage neutralization plate is disposed. The drainage neutralization plate is configured by consolidating a large number of chips with a cement-containing substance so that gaps are generated between the chips. The acidic water that has entered from the side surface is neutralized, the acidic water is drained in the in-plane direction within the cross-section, and the cement-containing substance of the drainable neutralizing plate is decomposed,
The arrangement area is a rectangular area, and the longitudinal direction of the arrangement area is an area that forms a predetermined angle on the slope with respect to the slope direction of the slope. A slope revegetation method, wherein the drainage means is installed on each outer side of the edge.
前記チップを木片で構成した請求項1記載の法面緑化方法。  The slope greening method according to claim 1, wherein the chip is made of wood.
JP2001209142A 2001-07-10 2001-07-10 Slope greening method Expired - Lifetime JP3935690B2 (en)

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