JP3236210B2 - Vegetation determination method and planting method for slope greening - Google Patents

Vegetation determination method and planting method for slope greening

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Publication number
JP3236210B2
JP3236210B2 JP05377396A JP5377396A JP3236210B2 JP 3236210 B2 JP3236210 B2 JP 3236210B2 JP 05377396 A JP05377396 A JP 05377396A JP 5377396 A JP5377396 A JP 5377396A JP 3236210 B2 JP3236210 B2 JP 3236210B2
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JP
Japan
Prior art keywords
vegetation
slope
tree species
species
planting
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.)
Ceased
Application number
JP05377396A
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Japanese (ja)
Other versions
JPH09220024A (en
Inventor
司 福嶋
章雄 上杉
惠之 瀬田
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Tobishima Corp
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Tobishima Corp
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  • Cultivation Of Plants (AREA)
  • Pit Excavations, Shoring, Fill Or Stabilisation Of Slopes (AREA)

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は法面緑化のための植
生決定方法及び植栽方法に係り、特に、法面周辺の生態
系を考慮して、法面における自然状態の復元を目指すよ
うにした法面緑化のための植生決定方法及び植栽方法に
関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a vegetation determination method and a planting method for revegetation on a slope, and more particularly, to restore a natural state on the slope in consideration of an ecosystem around the slope. The present invention relates to a vegetation determination method and a planting method for slope greening.

【0002】[0002]

【従来の技術】山間部等において土工作業を伴う工事を
行う場合には、必ずと言ってよいほど自然斜面に切土
面、盛土面が出現する。この場合、いままで比較的安定
した状態にあった自然斜面に手を加えたために、土砂の
流出、法面崩壊等の安定に関する問題が発生することが
予想される。従来、このような法面が発生した場所には
法面安定工が行われている。また、法面保護のため法面
緑化が行われることも多い。従来の法面緑化では、法面
に厚層基材を吹き付け、厚層基材面に芝類の播種を行っ
たり、イタチハギ,ヤマハギ等からなる低木林を造成し
たり、各種の牧草やメドハギを中心とした草本群落を造
成するのが一般的であった。
2. Description of the Related Art When a work involving earthwork is performed in a mountainous area or the like, a cut surface and an embankment surface appear on a natural slope as much as possible. In this case, since the natural slope which has been relatively stable until now has been modified, it is expected that problems relating to stability, such as runoff of soil and slope failure, will occur. Conventionally, slope stabilization has been performed in places where such a slope has occurred. In addition, slope greening is often performed to protect the slope. In conventional slope revegetation, a thick base material is sprayed on the slope, sowing lawns on the thick base material surface, creating a shrub forest consisting of weasels, yamahagi, etc., and various types of grass and meadowgi. It was common to create a herbaceous community at the center.

【0003】[0003]

【発明が解決しようとする課題】ところで、上述したよ
うな法面緑化工では、次のような問題点がある。 (1)草本群落を造成した場合 播種される草本には生長力が旺盛な種類が選択される。
このため、施工当初に急速に緑化が進むが、生長した草
本群落そのものは周囲の生態系、景観とはかけ離れたも
のである。また、厚層基材吹付工上に繁茂した草本群落
内に自生植物が侵入しにくいため、法面内での順調な植
生遷移が遅れる。 (2)低木林群落を造成した場合 イタチハギ,ヤマハギ等を主体とした落葉低木の群落を
造成した場合、夏期の緑量は増大するので法面全体とし
てボリューム感が得られ、周辺景観との違和感は少なく
なる。そのため景観面を考慮した場合には、ヤマハギを
主体とした低木林群落の造成が一般に奨励されている。
しかしながら、自然状態ではヤマハギやイタチハギの密
生した単純群落等は通常あり得ず、その後の植生遷移が
停滞してしまうことが懸念される。このため、法面に良
好な自然状態が形成されるかどうか疑問が残る。
However, the above-described slope revegetation has the following problems. (1) When a herbaceous community is created The seeds to be sown are selected from those with strong vigor.
For this reason, the greening progresses rapidly at the beginning of construction, but the growing herbaceous community itself is far from the surrounding ecosystem and landscape. In addition, the natural vegetation transition on the slope is delayed because the indigenous plants hardly invade into the herbaceous communities overgrown on the thick base material spraying work. (2) When a shrub forest community is created When a deciduous shrub community consisting mainly of weasels and yamahagi is created, the amount of greenery in summer increases, so that the entire slope has a sense of volume and discomfort with the surrounding landscape Is less. Therefore, in consideration of the landscape, the creation of shrub forest communities mainly composed of Yamahagi is generally encouraged.
However, in a natural state, densely populated simple communities of Yamahagi and Itachihagi are usually not possible, and there is a concern that subsequent vegetation transition will stagnate. Therefore, it remains questionable whether a good natural state is formed on the slope.

【0004】ところで、ダム工事等のように現場周辺に
出現する法面が大規模になる場合、実施される緑化工
は、ダム堤体付近の景観を大きく左右する。また法面部
分は観光客等によく目立つ場所であるため、この法面部
分における環境や生態系に対する配慮は、ダム全体の環
境配慮に対する評価に大きな影響を与えることが予想さ
れる。そこで、大規模な法面の出現が予想されるダム工
事において、前述した従来の法面緑化工の問題点を解消
するとともに、将来的な植生遷移を考慮して潜在自然植
生に近似した群落を構成する苗木を植栽するようにした
計画もある。しかし、この計画は植生遷移という経時的
な自然順応プロセスが省略されている上、法面周辺の自
然環境との係わりも考慮されていない。したがって、出
現した法面の周辺の従来の環境を十分配慮し、自然状態
の回復に寄与するような緑化を実現可能な植生の選定が
望まれる。
[0004] By the way, when the slope that appears around the site becomes large-scale such as dam construction, the revegetation that is performed greatly affects the landscape near the dam embankment. In addition, since the slope is a prominent place for tourists, etc., it is expected that consideration of the environment and ecosystem in this slope will greatly affect the evaluation of the entire dam for environmental consideration. Therefore, in dam construction where large-scale slopes are expected to appear, in addition to solving the problems of the conventional slope revegetation described above, considering the future vegetation transition, a community similar to latent natural vegetation will be created. There are also plans to plant the constituent seedlings. However, this plan omits the natural adaptation process of vegetation transition over time, and does not consider the relationship with the natural environment around the slope. Therefore, it is desired to select vegetation capable of realizing greening that contributes to the restoration of natural conditions, with due consideration given to the existing environment around the emerged slope.

【0005】そこで、本発明の目的は上述した従来の技
術が有する問題点を解消し、周辺の植物群落の中から法
面の環境に似た立地を考慮するようにした法面緑化のた
めの植生決定方法及び植栽方法を提供することにある。
[0005] Therefore, an object of the present invention is to solve the above-mentioned problems of the prior art and to consider a location similar to a slope environment from surrounding plant communities for greening a slope. It is to provide a vegetation determination method and a planting method.

【0006】[0006]

【課題を解決するための手段】上記目的を達成するため
に、本発明は法面緑化工を予定する切土法面の周辺地域
において、植物社会学的植生調査を複数調査地点で実施
し、この調査結果をもとに作成された植物群落組成表を
用いて土壌が薄く乾燥した立地に成立する群落を抽出
し、この群落を緑化工における目標とする植生タイプと
し、この植生タイプを構成する樹種について乾燥に強い
樹種とそれ以外の樹種とを前記植物群落組成表を用いて
判別し、判別された乾燥に強い複数の樹種を、前記法面
緑化工の植生における高木層、亜高木層、低木層、草本
層から構成される階層構造の各階層を構成する樹種とし
て、前記目標とする植生タイプにおける階層と樹種の関
係に基づいて割り振って導入することを特徴とする。
SUMMARY OF THE INVENTION In order to achieve the above object, the present invention relates to an area surrounding a cut slope where slope revegetation is planned.
Conducted phytosociological vegetation surveys at multiple survey points
And a plant community composition table created based on the survey results
Of communities established in locations where soil is thin and dry
And the target vegetation type for revegetation
And the species that make up this vegetation type
Tree species and other tree species using the plant community composition table
Discriminating and discriminating a plurality of identified tree species resistant to drying on the slope
Trees, sub-trees, shrubs, herbs in vegetation of revegetation
Tree species that make up each level of the hierarchical structure consisting of layers
The relationship between the hierarchy and tree species in the target vegetation type
It is characterized in that it is allocated and introduced based on the staff .

【0007】この植生決定方法で決定された複数の樹種
を、植栽する方法として厚層基材吹付工上に植栽するこ
とを特徴とする。
[0007] A plurality of tree species determined by this vegetation determination method
As a method for planting
And features.

【0008】[0008]

【0009】[0009]

【0010】[0010]

【0011】[0011]

【発明の実施の形態】以下、本発明の法面緑化のための
植生決定方法及び植栽方法の一実施の形態について添付
図面を参照して説明する。図1は、本発明の法面緑化の
ための植生決定方法及び植栽方法の一連作業手順を示し
た作業フローチャートである。以下、このフローチャー
トに基づいて説明を行う。まず、導入植生決定のプロセ
スについて説明する。このプロセスにおける最大の特徴
は、「乾燥し土壌の薄い立地」に成立する植生タイプを
構成する樹種の中から植栽の対象となる使用樹種を選び
出す点である。切土により軟岩等が露出したような法面
では、法面緑化工として所定厚の厚層基材吹付を行い植
生基盤を造成するが、この植生基盤は層厚が非常に薄く
法面勾配も急なため、十分な保水能力が得られず、乾燥
しがちとなる。このため、将来、法面上に周辺の現存植
生と同じような植生を成立させるには、周辺の自然中に
分布する様々な植生のうち「乾燥し土壌の薄い立地」に
成立している植生タイプをその目標植生として設定する
ことがポイントとなる。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, an embodiment of a vegetation determining method and a planting method for slope greening according to the present invention will be described with reference to the accompanying drawings. FIG. 1 is a work flowchart showing a series of work procedures of a vegetation determination method and a planting method for slope greening according to the present invention. Hereinafter, description will be made based on this flowchart. First, the process of determining the introduced vegetation will be described. The biggest feature of this process is that it selects the tree species to be planted from among the tree species that make up the vegetation type that is established in a "dry and thin soil location." On slopes where soft rocks, etc. are exposed due to cuts, a vegetation base is created by spraying a thick base material of a predetermined thickness as a slope greening work, but this vegetation base is extremely thin and has a slope of slope. Due to the steepness, sufficient water retention capacity cannot be obtained and tend to dry. For this reason, in order to establish vegetation similar to existing vegetation on the slope in the future, vegetation that is established in “dry and thin soiled locations” among various vegetation distributed in the surrounding nature The point is to set the type as its target vegetation.

【0012】そして、この目標植生を把握するために、
まず周辺の植生調査を行い、その結果を整理し、このよ
うな立地に成立する植生タイプを抽出し、どのような植
物で構成されているのかを明らかにする。さらに、樹種
の絞り込み作業を行い、最終的に残った乾燥に強いと考
えられる樹種のなかから植裁に使用する樹種を選定する
手法をとる。このとき植裁に使用する樹種は、実際の植
生タイプを構成する樹種のうちの一部にすぎないが、当
初植裁されたものが目標とする植生タイプの骨格とな
り、植裁されない構成種が後から自然に侵入してくるこ
とによって、次第に実際の植生タイプに近づいていくこ
とが予想される。
In order to grasp the target vegetation,
First, the surrounding vegetation is surveyed, the results are arranged, and the vegetation types that are established in such locations are extracted to clarify what kind of plants are composed. Furthermore, tree species are narrowed down, and a method is used to select a tree species to be used for planting from the finally remaining tree species that are considered to be resistant to drying. At this time, the tree species used for vegetation are only a part of the tree species that make up the actual vegetation type. It is expected that they will gradually approach the actual vegetation type by invading naturally later.

【0013】以下、実際に行った導入植生決定作業の例
をもとに、そのプロセス及び具体的な調査結果の内容に
ついて説明する。図2は、法面緑化を予定している現場
周辺を撮影した航空写真をもとに作成した植生図の一部
を模式的に示した説明図である。前述した「乾燥し土壌
の薄い立地」は、当該地域では主に山の尾根部及び岩露
頭地に分布することが、またそのような尾根部は主にア
カマツやキタゴヨウが優占するマツ林となっていること
が分かる。そこで、主にマツ林を対象に現場周辺の10
数地点の植生調査を行うことした。植生調査結果によ
って作成した出現種の植物群落組成表を表1に示した。
なお、植生調査は、植生研究分野で広く適用されている
植物社会学的植生調査法によって行った。
Hereinafter, the process and specific contents of the survey result will be described based on an example of an actually performed vegetation decision operation. FIG. 2 is an explanatory diagram schematically showing a part of a vegetation map created based on an aerial photograph taken around a site where a slope greening is planned. The above-mentioned `` locations with dry and thin soil '' are mainly distributed in mountain ridges and rocky outcrops in this area, and such ridges are mainly associated with pine forests dominated by red pine and northern pine. You can see that it has become. Therefore, mainly for pine forests, 10
It was decided to carry out a vegetation survey of the number of points. Table 1 shows a plant community composition table of emerging species created based on the vegetation survey results.
The vegetation survey was conducted using the phytosociological vegetation survey method widely applied in the field of vegetation research.

【0014】[0014]

【表1】 [Table 1]

【0015】この植物群落組成表は横軸に調査地点が、
縦軸に植物種名がとられており、表中の枠で囲まれた数
字及び記号は各調査地点における各植物の被度(量を表
す指標)を表している。なお、この植物群落組成表は同
じような出現傾向を示す種同士及び同じような種組成を
持つ調査地点同士が近くなるように考慮してデータ行列
を並べ換え、データの適正化を図った結果を示したもの
である。また、表の左側に乾燥傾向の植生タイプ、右側
に湿潤傾向の植生タイプがくるように並べてある。この
植物群落組成表から、表上部の種群(枠に囲まれた部
分)が乾燥した立地する、すなわち「乾燥に強い種類」
であることを特徴づける種群であり、その下の右側に被
度の数値が固まって並んでいる種群が適潤及び過湿な立
し、すなわち「乾燥にそれほど強くない種類」を特徴
づける種群であることが推察できる。この適湿な立地に
も生育するものは、「乾燥にそれほど強くない種類」と
考えて消去する等の判別作業を行った。このようにして
乾燥に強く、当該地域において切土法面の環境に適応可
能樹種として抽出された樹種を、高木層、亜高木層、低
木層、草本層ごとに階層を構成するようにして表−2に
示した。
[0015] In this plant community composition table, the survey points are shown on the horizontal axis,
The vertical axis represents the plant species name, and the numbers and symbols surrounded by the frames in the table represent the coverage (index indicating the amount) of each plant at each survey point. Note that this plant community composition table rearranges the data matrix in consideration of species with similar appearance tendencies and survey points with similar species composition to be close to each other, and optimizes the data. It is shown. In addition, the vegetation types tend to be dry on the left side of the table and the vegetation types tend to be wet on the right side. this
From the plant community composition table, the species group at the top of the table (the part surrounded by the frame) is located in a dry location, that is, "a kind resistant to drying"
A seed group characterizing that this is, situated species group are arranged solidified is numeric severity on the right such TekiJun and excessive moisture under it, i.e. at the species group characterizing the "less intense kinds drying" It can be inferred that there is. Those that grew even in this humid location were discriminated such as erasing them, considering them as "not so strong in drying" . Like this
Tree species that are resistant to drought and can be adapted to the environment of the cut slope in the area are identified as tree species , sub-tree species,
Table 2 shows the tree layers and herbaceous layers, each having a hierarchy .

【0016】[0016]

【表2】 [Table 2]

【0017】さらに、表−2に示した適応可能樹種のう
ち、法面の規模や現地に搬入できる苗木の生産状況を考
慮し、最終的に植栽に使用する樹種を選定する。なお、
導入樹種が生長するまでの当面の間に、雑草が繁茂しな
いようにマルチングを計画する。このマルチングに用い
る材料としては人工的なものでもよいし、ナデシコ類、
クローバー類等の草本を厚層基材吹付工で播種してもよ
い。
Further, among the applicable tree species shown in Table 2, the tree species finally used for planting is selected in consideration of the scale of the slope and the production status of the seedlings that can be carried to the site. In addition,
Mulching will be planned so that weeds will not grow until the introduced tree species grows. The material used for this mulching may be artificial, nadesico,
Herbs such as clovers may be sown by a thick-layer base material sprayer.

【0018】次に、以上のプロセスで計画された導入植
生を法面に植栽する植栽プロセスについて説明する。ま
ず、法面に構築された法枠内に金網(ラス網)等を張り
付ける。作業手順によっては、あらかじめ金網等を張り
付けた部分に法枠を構築してもよい。次いで、金網等の
上に植生基材を吹き付けて下地とする。その上に樹木お
よびツル植物の苗木を置き、支柱等で法面上に固定す
る。さらに2度目の吹付けを行い、苗木の根鉢を基材で
覆うとともに、所定厚さまで吹き付ける。導入苗木の十
分な生育のために、充分な量の土壌(基材)を使用す
る。本実施の形態では、法枠の水平梁上に植生基材を吹
き溜めることによって苗木導入を確実なものとしてい
る。植生基材には肥料分の多い有機質を主体としたもの
ではなく、導入する自然樹種が適切に生育するように肥
料分の少ない砂質系厚層基材吹付工を使用することが好
ましい。また、この砂質系厚層基材吹付工の耐浸食性を
向上させるために、短繊維を混入することも好ましい。
さらに、法枠の下側に吸い出し防止用マットを敷設し、
基材底部に雨水等がたまるのを防止することも好まし
い。
Next, a planting process for planting the introduced vegetation planned on the above process on the slope will be described. First, a wire net (lath net) or the like is attached to the inside of the law frame constructed on the slope. Depending on the work procedure, a legal frame may be constructed in a portion to which a wire mesh or the like is attached in advance. Next, a vegetation base material is sprayed on a wire net or the like to form a base. Trees and saplings of vine plants are placed on top of them, and fixed on the slope with props or the like. Further, a second spraying is performed to cover the root pot of the seedlings with the base material and spray to a predetermined thickness. Use sufficient soil (substrate) for sufficient growth of the introduced seedlings. In the present embodiment, the seedlings are reliably introduced by blowing the vegetation base material on the horizontal beams of the legal frame. The vegetation base material is not mainly composed of organic matter containing a large amount of fertilizer, and it is preferable to use a sandy thick layer base material spraying method with a small amount of fertilizer so that the natural tree species to be introduced grows appropriately. It is also preferable to mix short fibers in order to improve the erosion resistance of this sandy thick layer base material spraying work.
In addition, lay a mat for preventing suction under the legal framework,
It is also preferable to prevent rainwater or the like from collecting on the bottom of the base material.

【0019】次いで、表−2で示された高木、亜高木、
低木ごとに生産状況等を考慮して樹種を選択した苗木を
植栽する。各種の樹種を導入することによって法面植生
全体が苗木の段階で階層構造を形成するようにする。こ
のとき各階層が一種の樹種のみにならないように、でき
るだけ多くの樹種を選択するのが好ましい。植裁密度
は、隣接した苗木がお互いに被陰し合わないように、ま
た周辺から自生植物が侵入できる程度とすることが好ま
しい。本実施の形態では、一例として1本/m2程度と
した。なお、導入苗木が供給可能となるまでの育苗期間
を考慮して植栽計画をたてることが重要である。また、
苗木を植栽し、根が十分活着していないうちに降雪のお
それがある場合には、支柱等を添えて苗の固定をするこ
とも好ましい。
Next, the Takagi, sub-Takagi,
Seedlings are selected for each shrub, taking into account the production status and other factors. By introducing various tree species, the whole slope vegetation will form a hierarchical structure at the seedling stage. At this time, it is preferable to select as many tree species as possible so that each hierarchy does not include only one tree species. The planting density is preferably such that adjacent seedlings do not shade each other and that native plants can invade from the periphery. In the present embodiment, as one example, the number is set to about 1 / m 2 . It is important to make a planting plan in consideration of the nursery period until the seedlings can be supplied. Also,
If there is a possibility of snowfall before the roots of the seedlings have been planted and the roots are not fully established, it is also preferable to fix the seedlings with supporting columns or the like.

【0020】導入苗木は原則としてコンテナ(ポット)
苗木を用い、植裁後の活着を確実なものにするために、
出荷時に圃場において熟練工が枝葉を切り詰めて切り戻
しコンテナ苗木の状態で出荷する。さらに、導入苗木が
樹木として生長するまでの当面の間、土壌表面の侵食防
止には、ナデシコ類・クローバー等の草本を厚層基材吹
付工で播種することで対応する。これらの草本は背丈が
低いため、樹木の生育を妨げず、また樹木が十分に生育
すると樹木に被陰され衰退あるいは枯死することが予想
される。このため林床には周辺からの自然植生の侵入が
可能となる。併せて景観対策等を目的として法枠の早期
被覆を図ることも好ましい。法枠を被覆するツル植物の
一例としてナツヅタを、法枠延長に対して1本/m程度
の密度で植裁する。
Introduced seedlings are in principle containers (pots)
Using seedlings, in order to ensure survival after planting,
At the time of shipment, a skilled worker cuts the leaves and leaves in the field and ships them back in a container seedling state. Further, for the time being, until the introduced seedlings grow as trees, erosion prevention on the soil surface is dealt with by sowing a herbaceous plant, such as dianthus and clover, with a thick-layer base material spraying method. Since these herbs are short, they do not hinder the growth of trees, and when the trees grow sufficiently, they are expected to be shaded by the trees and to die or die. For this reason, natural vegetation can enter the forest floor from the surroundings. At the same time, it is also preferable to cover the legal framework early for the purpose of landscape measures. As an example of a vine plant that covers the stake, vines are planted at a density of about 1 / m with respect to the extension of the stake.

【0021】図3〜図6は、1辺2m、梁厚30cm程
度の吹付法枠10の水平梁11上に吹き付ける厚層基材
12の形状、吹付厚を異ならせた2種の施工例を示した
ものである。施工当初(図3、図5)と10年後におけ
る予想植生状態(図4、図6)の各図から植栽後10年
の年月を経る間にアカマツ、リョウブ等の高木20、亜
高木21がある程度の樹高まで生長し、林床では周辺か
らの侵入植生22が生長し、全体として周辺の植生環境
と類似した階層構造が形成されることが期待できる。図
7、図8は1辺3m、梁厚75cm程度の大型の現場打
ち法枠15に本発明の導入植生を植栽した例と、10年
後の予想植生状態を示した模式説明図である。このよう
に法枠の形状、寸法の相違に応じて厚層基材の吹付形状
や植栽配置を変更することにより厚層基材の使用量も軽
減でき、また植栽当初の苗木の見栄えも十分確保でき
る。また、数年のうちに大きな法枠もナツヅタ23の生
長により被覆されてしまうことが予想される。
FIGS. 3 to 6 show two examples in which the shape and thickness of the thick base material 12 sprayed on the horizontal beam 11 of the spraying method frame 10 having a side length of 2 m and a beam thickness of about 30 cm are different. It is shown. From the figures of the expected vegetation state at the beginning of construction (Figs. 3 and 5) and 10 years later (Figs. 4 and 6), during the 10 years after planting, trees 20 such as Japanese red pine, Ryobu, etc. It is expected that 21 grows to a certain tree height and invasive vegetation 22 grows from the surroundings on the forest floor, and a hierarchical structure similar to the surrounding vegetation environment is formed as a whole. FIGS. 7 and 8 are schematic explanatory views showing examples in which the introduced vegetation of the present invention is planted in a large-scale cast-in-place frame 15 having a side of 3 m and a beam thickness of about 75 cm, and a predicted vegetation state 10 years later. . In this way, by changing the spraying shape and planting arrangement of the thick base material according to the difference in the shape and size of the legal frame, the usage of the thick base material can be reduced, and the appearance of the seedlings at the beginning of planting can also be reduced. We can secure enough. In addition, it is expected that a large legal framework will be covered by the growth of the nuts 23 within a few years.

【0022】なお、以上の説明では、切土によって出現
した法面の法面緑化のための植生決定方法及び植栽方法
について述べたが、切土法面と同様に出現する可能性が
ある盛土法面においても、以上の植生決定プロセスを適
用でき、盛土法面において予想される地盤状態に類似し
た周辺の植生を抽出できることは言うまでもない。
In the above description, the vegetation determination method and the planting method for slope greening of the slope that has appeared due to the cut have been described. However, the embankment that may appear similarly to the cut slope has been described. It goes without saying that the above-described vegetation determination process can be applied to a slope, and that surrounding vegetation similar to the expected ground state on the embankment slope can be extracted.

【0023】[0023]

【発明の効果】以上の説明から明らかなように、本発明
によれば、出現した法面の周辺の環境を考慮し、自然の
生態系にかなった植生環境を将来にわたって復元するこ
とができるという効果を奏する。
As is apparent from the above description, according to the present invention, it is possible to restore a vegetation environment suitable for a natural ecosystem in the future in consideration of the environment around the slope that has appeared. It works.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明による法面緑化のための植生決定方法及
び植栽方法の一実施の形態を示した作業フローチャー
ト。
FIG. 1 is a work flowchart illustrating an embodiment of a vegetation determination method and a planting method for slope greening according to the present invention.

【図2】本発明の法面緑化のための植生決定プロセスに
おいて作成される植生図を模式的に示した説明図。
FIG. 2 is an explanatory diagram schematically showing a vegetation map created in a vegetation determination process for slope greening according to the present invention.

【図3】本発明の植生決定方法によって選定された導入
樹種を、吹付法枠に植栽した実施の一態様を示した模式
説明図(施工当初)。
FIG. 3 is a schematic explanatory view showing an embodiment in which an introduced tree species selected by the vegetation determination method of the present invention is planted in a spraying method frame (at the beginning of construction).

【図4】図3に示した導入植生の10年後の植生状態を
示した模式説明図。
FIG. 4 is a schematic explanatory view showing a vegetation state 10 years after the introduced vegetation shown in FIG. 3;

【図5】本発明の植生決定方法によって選定された導入
樹種を、吹付法枠に植栽した実施の他の態様を示した模
式説明図(施工当初)。
FIG. 5 is a schematic explanatory view showing another aspect of the embodiment in which the introduced tree species selected by the vegetation determination method of the present invention is planted in a spraying method frame (at the beginning of construction).

【図6】図5に示した導入植生の10年後の植生状態を
示した模式説明図。
FIG. 6 is a schematic explanatory view showing a vegetation state 10 years after the introduced vegetation shown in FIG. 5;

【図7】本発明の植生決定方法によって選定された導入
樹種を、大型現場打ち法枠に植栽した実施の他の態様を
示した模式説明図(施工当初)。
FIG. 7 is a schematic explanatory view showing another embodiment in which the introduced tree species selected by the vegetation determination method of the present invention is planted in a large-scale cast-in-place method (at the beginning of construction).

【図8】図7に示した導入植生の10年後の植生状態を
示した模式説明図。
FIG. 8 is a schematic explanatory view showing a vegetation state 10 years after the introduced vegetation shown in FIG. 7;

【符号の説明】[Explanation of symbols]

10 吹付法枠 11 水平梁 12 厚層基材 15 現場打ち法枠 20 高木 21 亜高木 22 侵入植生 DESCRIPTION OF SYMBOLS 10 Spraying method frame 11 Horizontal beam 12 Thick layer base material 15 Cast-in-place method frame 20 Takagi 21 Sub-takagi 22 Invasive vegetation

フロントページの続き (72)発明者 瀬田 惠之 東京都千代田区三番町2番地 飛島建設 株式会社内 (58)調査した分野(Int.Cl.7,DB名) A01G 7/00 A01G 1/00 E02D 17/20 Continuation of the front page (72) Inventor Yoshiyuki Seta 2 Sanbancho, Chiyoda-ku, Tokyo Tobishima Construction Co., Ltd. (58) Field surveyed (Int. Cl. 7 , DB name) A01G 7/00 A01G 1/00 E02D 17/20

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】法面緑化工を予定する切土法面の周辺地域
において、植物社会学的植生調査を複数調査地点で実施
し、この調査結果をもとに作成された植物群落組成表を
用いて土壌が薄く乾燥した立地に成立する群落を抽出
し、この群落を緑化工における目標とする植生タイプと
し、この植生タイプを構成する樹種について乾燥に強い
樹種とそれ以外の樹種とを前記植物群落組成表を用いて
判別し、判別された乾燥に強い複数の樹種を、前記法面
緑化工の植生における高木層、亜高木層、低木層、草本
層から構成される階層構造の各階層を構成する樹種とし
て、前記目標とする植生タイプにおける階層と樹種の関
係に基づいて割り振って導入することを特徴とする植生
決定方法。
1. The area around the cut slope where the slope greening is planned
Conducted phytosociological vegetation surveys at multiple survey points
And a plant community composition table created based on the survey results
Of communities established in locations where soil is thin and dry
And the target vegetation type for revegetation
And the species that make up this vegetation type
Tree species and other tree species using the plant community composition table
Discriminating and discriminating a plurality of identified tree species resistant to drying on the slope
Trees, sub-trees, shrubs, herbs in vegetation of revegetation
Tree species that make up each level of the hierarchical structure consisting of layers
The relationship between the hierarchy and tree species in the target vegetation type
A vegetation determination method characterized in that the vegetation is allocated and introduced based on a staff member .
【請求項2】請求項1で決定された複数の樹種を、厚層
基材吹付工上に植栽したことを特徴とする法面緑化のた
めの植栽方法。
2. A planting method for slope greening, wherein a plurality of tree species determined in claim 1 are planted on a thick base material spraying work.
JP05377396A 1996-02-16 1996-02-16 Vegetation determination method and planting method for slope greening Ceased JP3236210B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP05377396A JP3236210B2 (en) 1996-02-16 1996-02-16 Vegetation determination method and planting method for slope greening

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP05377396A JP3236210B2 (en) 1996-02-16 1996-02-16 Vegetation determination method and planting method for slope greening

Publications (2)

Publication Number Publication Date
JPH09220024A JPH09220024A (en) 1997-08-26
JP3236210B2 true JP3236210B2 (en) 2001-12-10

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ID=12952145

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Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP3236210B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000139113A (en) * 1998-11-11 2000-05-23 Sumitomo Forestry Co Ltd Afforestation of deserted land
JP5967398B2 (en) * 2011-06-13 2016-08-10 清水建設株式会社 Planting method
JP6875674B2 (en) * 2016-09-16 2021-05-26 大成建設株式会社 Green space construction method
CN106446434A (en) * 2016-09-30 2017-02-22 深圳前海弘稼科技有限公司 Method and device for determining plantable plants
CN106941901A (en) * 2017-02-28 2017-07-14 南阳师范学院 Cold drought-hit area gentle slope type tunnel portal plant Li planting and establishing methods
CN110490478B (en) * 2019-08-26 2023-04-07 贵州大学 Road street tree pool ecological environment investigation method
CN116137987A (en) * 2023-02-17 2023-05-23 黄河勘测规划设计研究院有限公司 Ecological restoration method for soil sampling field

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Publication number Publication date
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