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JP4067100B2 - Sediment flow method - Google Patents
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JP4067100B2 - Sediment flow method - Google Patents

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JP4067100B2
JP4067100B2 JP2003291994A JP2003291994A JP4067100B2 JP 4067100 B2 JP4067100 B2 JP 4067100B2 JP 2003291994 A JP2003291994 A JP 2003291994A JP 2003291994 A JP2003291994 A JP 2003291994A JP 4067100 B2 JP4067100 B2 JP 4067100B2
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sand
earth
film
forming agent
membrane
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ブーン ケン リン
裕美 新保
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Kajima Corp
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本発明は土砂の搬送方法に関し、とくに土砂を水流に浮かべて搬送する方法に関する。   The present invention relates to a method for conveying earth and sand, and more particularly, to a method for conveying earth and sand floating in a water stream.

ダム等の貯水池では、上流から流入する土砂の堆積が進行すると有効貯水容量が減少すると共に下流の河川・海岸の浸食進行等を招くため、貯水池の恒久的利用や河川・海岸の土砂環境改善等を目的として、貯水池内に堆積した土砂(以下、堆砂ということがある。)を適宜下流へ排出・供給することが求められる。例えば大雨等の出洪水時に堆砂を流水と共に下流へ流下させる方法等が開発されているが、大量の堆砂を一挙に下流へ排出すると下流の生物生息環境に大きな影響を与えるおそれがある。そのため従来から、浚渫船・パイプ吸引・コンベア等により貯水池から堆砂を搬出し、搬出した堆砂をダンプトラック等により下流の適当な位置へ運搬し、生物生息環境に影響を与えないように撒き出す方法が実施されている。   In reservoirs such as dams, the accumulation of sediment flowing in from the upstream will reduce the effective water storage capacity and cause erosion of downstream rivers and coasts, etc., so the permanent use of reservoirs and improvement of sediment environment in rivers and coasts, etc. For this purpose, it is required to discharge and supply the sediment accumulated in the reservoir (hereinafter sometimes referred to as sediment) to the downstream as appropriate. For example, a method has been developed in which sediment is allowed to flow downstream along with running water during floods such as heavy rain. However, if a large amount of sediment is discharged to the downstream at once, there is a possibility that it will greatly affect the biological habitat environment downstream. Therefore, conventionally, sediment is carried out from the reservoir by dredgers, pipe suction, conveyors, etc., and the carried sediment is transported to an appropriate downstream position by a dump truck, etc., so that it does not affect the biological habitat environment. The method has been implemented.

特許文献1は、ダム貯水池から採取した堆砂を結合強度の小さい固化剤と混合して崩壊性ブロックを製造し、その崩壊性ブロックを水制工等の構造物としてダム下流側の流域に配置するダム堆砂の処理方法を開示する。また特許文献2は、ダム堆砂を骨材とし、結合材、セメントと混和材、又はセメントと破砕材を配合して作成した崩壊性コンクリートブロックをダム下流側に配置するダム堆砂の処理方法を提案している。これらの崩壊性ブロック(コンクリートブロック)は、水の浸透作用や衝撃力、凍結融解の繰り返しにより短期間で崩壊し、堆砂を崩壊砂として徐々に放出するので、堆砂を自然に近い状態で下流へ供給することができる。   Patent Document 1 manufactures a collapsible block by mixing sediment collected from a dam reservoir with a solidifying agent having a low bond strength, and arranges the collapsible block as a structure such as a water control system in the basin downstream of the dam. Disclosed is a method for treating dam deposits. Patent Document 2 discloses a method for treating dam sediment, in which a collapsible concrete block prepared by combining dam sediment with aggregate, cement, admixture, or cement and crushed material is disposed on the downstream side of the dam. Has proposed. These collapsible blocks (concrete blocks) disintegrate in a short period of time due to water penetration, impact force, and repeated freezing and thawing, and gradually release the sediment as disintegrated sand. It can be supplied downstream.

特開平6−073717号公報Japanese Patent Laid-Open No. 6-073717 特開平6−157107号公報JP-A-6-157107

しかし、特許文献1及び2の方法は、堆砂のうち比較的粒径の大きい砂や石を下流へ供給するためには有効であるが、小粒径の泥分やシルト分(以下、これらを纏めて泥分ということがある。)は骨材としての利用が難しいため、泥分を下流へ供給するには適していない。砂や石のみを下流に供給したのでは、下流の土砂環境(例えば、土砂の粒度分布等)を適切に改善することは難しい。また、骨材として利用が難しい泥分をそのまま下流へ放流すると、河川のCOD(化学的酸素消費量)や濁度が上昇し、河川魚(鮎等)の餌となる藻類の繁殖環境や河床の水生昆虫の生息環境を悪化させるおそれがある。泥分をダンプトラック等に積載して下流へ運搬することも考えられるが、その場合は運搬中に乾燥した泥分が飛散し、新たな粉塵問題等が起こるおそれがある。泥分を砂や石と共に下流へ供給できる技術の開発が望まれている。   However, the methods of Patent Documents 1 and 2 are effective for supplying sand and stones having a relatively large particle size among sediments to the downstream, but small mud and silt components (hereinafter referred to as these). ) Is not suitable for supplying the mud downstream. If only sand and stones are supplied downstream, it is difficult to properly improve the downstream sediment environment (for example, the particle size distribution of the sediment). In addition, if mud that is difficult to use as aggregate is discharged downstream, the COD (chemical oxygen consumption) and turbidity of the river will rise, and the algae breeding environment and riverbed that will feed the river fish (such as salmon) May worsen the aquatic insect habitat. It is conceivable that the mud is loaded on a dump truck or the like and transported downstream, but in that case, the dried mud may be scattered during transport, which may cause a new dust problem. Development of technology that can supply mud with sand and stones downstream is desired.

また、特許文献1及び2の方法は、製造した崩壊性ブロックを下流へ運搬するための輸送エネルギーが必要であり、大量の堆砂を下流へ運搬するために膨大な輸送エネルギーを必要とする。例えば大量の崩壊性ブロックをダンプトラック等で運搬する場合は、輸送エネルギーを必要とするだけでなく、騒音やC02排出等の環境上の問題も生じる。このように大量の土砂を経済的に搬送することは、貯水池の堆砂対策だけでなく、土工事等で発生する土砂対策においても重要な課題となっている。 Moreover, the method of patent document 1 and 2 requires the transportation energy for conveying the manufactured collapsible block downstream, and requires enormous transportation energy in order to convey a large amount of sediment. For example, when transporting large amounts of disintegrating blocks dump truck or the like, not only requires transportation energy also results in environmental problems such as noise and C0 2 emissions. Economic transportation of a large amount of earth and sand in this way is an important issue not only for countermeasures against sedimentation in reservoirs but also for countermeasures against earth and sand generated by earth work.

そこで本発明の目的は、泥分が含まれる土砂を経済的に搬送する水流浮上式搬送方法を提供することにある。   SUMMARY OF THE INVENTION An object of the present invention is to provide a water flow floating transport method that economically transports earth and sand containing mud.

図1及び図4の実施例を参照するに、本発明による土砂の水流浮上式搬送方法は、土砂2を発泡剤12と共に膜11に封入し発泡剤12から発生する気泡13により土砂2を水流7に浮かべて搬送してなるものである。 Referring to the embodiment of FIG . 1 and FIG. 4, in the method of conveying the earth and sand according to the present invention, the earth and sand 2 is enclosed in the film 11 together with the foaming agent 12 , and the earth and sand 2 is formed by the bubbles 13 generated from the foaming agent 12. It floats on the water stream 7 and is conveyed.

更に好ましくは、発泡剤12の量を、土砂2の搬送予定距離と水流7の流速と膜11の気密性とに応じて調整する。例えば発泡剤12の量を、土砂2が予定距離だけ搬送されたのち膜11と共に水底へ沈むように調整することができる。また、予定距離だけ搬送された土砂2を膜11と共に水流7から回収し、膜溶解剤21により膜11を溶かして土砂2を取り出すことも可能である。   More preferably, the amount of the foaming agent 12 is adjusted according to the planned transport distance of the earth and sand 2, the flow velocity of the water flow 7, and the airtightness of the membrane 11. For example, the amount of the foaming agent 12 can be adjusted so that the earth and sand 2 are transported a predetermined distance and then sink to the bottom of the water together with the film 11. It is also possible to collect the earth and sand 2 transported for a predetermined distance from the water flow 7 together with the film 11, dissolve the film 11 with the film dissolving agent 21, and take out the earth and sand 2.

本発明による土砂の水流浮上式搬送方法は、土砂を発泡剤と共に膜(以下、コーティング膜ということがある。)に封入し、発泡剤から発生する気泡により土砂を水流に浮かべて所要位置まで搬送するので、次の顕著な効果を奏する。 According to the present invention, the method of conveying the earth and sand by floating it encloses the earth and sand together with a foaming agent in a film (hereinafter sometimes referred to as a coating film), and floats the earth and sand on the water stream by bubbles generated from the foaming agent and conveys it to a required position. Therefore, the following remarkable effects are produced.

(イ)土砂を、河川等の自然の水流を利用して、人為的にエネルギーを加えることなく省エネルギー的・経済的に所要位置まで搬送することができる。
(ロ)砂や石だけでなく泥分も併せて搬送できるので、下流の河川・海岸の土砂環境の改善に有効に利用できる。
(ハ)ダム貯水池の堆砂対策だけでなく、泥分等が多量に発生する地盤削孔等の土工事現場やトンネル工事現場等における土砂の搬送に有効に利用できる。
(ニ)土砂を膜に封入して搬送するので、河川等を利用した場合でもCODや濁度の上昇といった環境上の問題を生じる危険が小さい。
(ホ)また、従来のトラック等による土砂の搬送に比し騒音やC02排出等の環境上の問題を生じるおそれがなく、極めてクリーンな搬送方法といえる。
(ヘ)気泡を生じる発泡剤を利用して土砂を水流に浮かべて搬送するので、発泡剤の量の調節により土砂の搬送距離を調整し、土砂を下流の所要位置に沈めることができる。
(ト)自然界(海域や河川域等)で分解され易い材料製の膜を用いることにより、たとえ土砂が膜と共に水底に沈降した場合でも水域への負荷を十分小さく抑えることができる。
(B) The earth and sand can be transported to the required position in an energy-saving and economical manner by using natural water currents such as rivers without artificially applying energy.
(B) Since not only sand and stone but also mud can be transported together, it can be effectively used to improve the sediment environment of downstream rivers and coasts.
(C) It can be used effectively not only for sedimentation measures in dam reservoirs but also for transporting earth and sand at ground construction sites such as ground drilling and tunnel construction sites where a large amount of mud is generated.
(D) Since soil and sand are enclosed in a film and transported, the risk of environmental problems such as increased COD and increased turbidity is small even when rivers are used.
(E) In addition, there is no possibility of causing environmental problems in noise and C0 2 emissions or the like relative to the transport of sediment by conventional track such, it can be said that an extremely clean transfer method.
(F) Since the earth and sand are floated and conveyed using a foaming agent that generates bubbles, the distance of earth and sand can be adjusted by adjusting the amount of the foaming agent, and the earth and sand can be submerged at a required position downstream.
(G) By using a film made of a material that is easily decomposed in the natural world (sea area, river area, etc.), even when earth and sand settles on the bottom of the water together with the film, the load on the water area can be suppressed sufficiently small.

図1は、ダム貯水池1の堆砂を下流の河川域・海域へ供給する場合に適用した本発明の実施例を示す。図示例では、この場合堆砂である土砂2を浚渫船・吸引パイプ・コンベア等の採取装置4により貯水池1から採取し、添加装置5により低比重物質16を添加したのち、コーティング装置6によりコーティング膜11で包む。低比重物質16と共に膜11に包んだ土砂2を、この場合河川である自然の水流7に放流し、河口その他の所要位置まで浮遊させて搬送し、下流の所要位置において土砂2を膜11と共に回収するか又は膜11と共に水底へ沈降させる。本発明は、泥分を砂や石と共に膜11に封入して下流へ供給できるので、河川・海岸の土砂環境改善等を目的した堆砂対策に有効である。但し、本発明は堆砂2の搬送に限定されず、例えば土工事現場やトンネル工事現場等において発生する土砂2の搬送にも適用できる。また、水流7も河川等の自然の流れに限定されず、適当な人工の水流7を利用できる。   FIG. 1 shows an embodiment of the present invention applied to the case where sedimentation in the dam reservoir 1 is supplied to a downstream river area / sea area. In the illustrated example, the earth and sand 2 which is sediment in this case is collected from the reservoir 1 by a collecting device 4 such as a dredger, a suction pipe and a conveyor, and a low specific gravity substance 16 is added by an adding device 5 and then a coating film is formed by a coating device 6. Wrap with 11. The sediment 2 wrapped in the membrane 11 together with the low specific gravity material 16 is discharged into a natural water stream 7 which is a river in this case, suspended and transported to the estuary and other required positions, and the sediment 2 is transported together with the membrane 11 at the downstream required location. Collect or settle to bottom with membrane 11. In the present invention, mud can be enclosed in the membrane 11 together with sand and stones and supplied downstream, which is effective for measures against sedimentation for the purpose of improving the sediment environment of rivers and coasts. However, the present invention is not limited to the conveyance of the sediment 2 but can also be applied to the conveyance of the earth and sand 2 generated at, for example, an earthwork site or a tunnel construction site. The water flow 7 is not limited to a natural flow such as a river, and an appropriate artificial water flow 7 can be used.

図2は、貯水池1から採取した土砂2をコーティング膜11に封入して水流7へ放流するまでの流れ図の一例を示す。この例ではコーティング装置6に、膜化剤15と、膜化剤15との反応により膜11を形成する膜形成剤14とを含めている。土砂2を膜形成剤14と混合した上で膜化剤15中に浸すことにより膜11で封入する。膜形成剤14の一例はアルギン酸、カルボキシメチルセルロース(CMC)、ペクチン溶液等のカルボキシル基を有する多糖類であり、膜化剤15の一例はカルシウムイオン溶液(例えば、水酸化カルシウム水溶液)である。アルギン酸は海草からの抽出材料であり、他の多糖類も食品添加物等として使用されるものであり、何れも生分解可能な材料である。   FIG. 2 shows an example of a flow chart until the earth and sand 2 collected from the reservoir 1 is enclosed in the coating film 11 and discharged into the water stream 7. In this example, the coating apparatus 6 includes a film forming agent 15 and a film forming agent 14 that forms the film 11 by a reaction with the film forming agent 15. The earth and sand 2 are mixed with the film forming agent 14 and immersed in the film forming agent 15 to be enclosed with the film 11. An example of the film forming agent 14 is a polysaccharide having a carboxyl group such as alginic acid, carboxymethyl cellulose (CMC), or a pectin solution, and an example of the film forming agent 15 is a calcium ion solution (for example, an aqueous calcium hydroxide solution). Alginic acid is a material extracted from seaweed, and other polysaccharides are used as food additives and the like, and all are biodegradable materials.

図2に示す膜形成剤14と膜化剤15との反応によりコーティング膜11を形成する方法は、土砂2を含水状態のまま膜11へ封入できるので、泥分が含まれる土砂2を半乾燥状態のまま膜11へ簡単に封入できる利点がある。また後述するように、膜形成剤14の濃度や混合量を調節することにより、例えば搬送途中に岩等との衝突に耐えられる程度にコーティング膜11の厚さや強度を調整できる。更に、膜11を生分解可能な材料製とすることにより、たとえ膜11が水流7中に分散した場合でも自然界における分解を期待でき、環境面での安全性を確保しつつ膜封入土砂10を自然に崩壊させて土砂2を下流域へ供給することができる。但し、図示例のコーティング膜11に代えて、例えば強化ゴム樹脂製のカプセル、水溶性ビニロンフィルムの膜等を使用してもよい。   In the method of forming the coating film 11 by the reaction of the film forming agent 14 and the film forming agent 15 shown in FIG. 2, the earth and sand 2 can be enclosed in the film 11 in a water-containing state, so that the mud-containing earth and sand 2 is semi-dried. There is an advantage that it can be easily sealed in the film 11 in the state. As will be described later, the thickness and strength of the coating film 11 can be adjusted to such an extent that the film forming agent 14 can withstand a collision with a rock or the like during conveyance by adjusting the concentration and the mixing amount of the film forming agent 14. Furthermore, by making the membrane 11 made of a biodegradable material, even when the membrane 11 is dispersed in the water stream 7, it can be expected to decompose in nature, and the membrane-enclosed earth and sand 10 is secured while ensuring environmental safety. The earth and sand 2 can be supplied to the downstream area by being naturally collapsed. However, instead of the coating film 11 shown in the figure, for example, a capsule made of a reinforced rubber resin, a water-soluble vinylon film, or the like may be used.

また図2の例では、土砂2を水面に浮かべるための低比重物質16として発泡剤12が発生する気泡13を用いている(図4も参照)。発泡剤12として従来技術に属する様々なものが利用できるが、例えば酒石酸(C4H6O6)及び重曹(NaHCO3)を含み二酸化炭素(CO2)を発生するものとすることができる。酒石酸及び重曹を含む発泡剤12は、人の胃X線検査等の造影剤等に使用されるものであり、たとえ水流7に分散した場合でも汚染源となり難い。但し、発泡剤12に代えて、気体をそのままコーティング膜11に封入してもよく、その他の適当な低比重物質16を用いて土砂2を水面に浮上させることができる。 In the example of FIG. 2, bubbles 13 in which a foaming agent 12 is generated are used as the low specific gravity material 16 for floating the earth and sand 2 on the water surface (see also FIG. 4). Various blowing agents 12 belonging to the prior art can be used. For example, tartaric acid (C 4 H 6 O 6 ) and sodium bicarbonate (NaHCO 3 ) can be used to generate carbon dioxide (CO 2 ). The foaming agent 12 containing tartaric acid and baking soda is used as a contrast agent for human stomach X-ray examination and the like, and even if dispersed in the water stream 7, it is unlikely to become a source of contamination. However, instead of the foaming agent 12, the gas may be enclosed in the coating film 11 as it is, and the earth and sand 2 can be floated on the water surface by using other appropriate low specific gravity substances 16.

図2のステップ201において貯水池1から土砂2をすくい上げ、必要に応じて水分をある程度乾燥させる。ステップ202において、例えばアルギン酸ナトリウム水溶液、CMCナトリウム水溶液等の膜形成剤14を水に溶かして所要濃度の水溶液を調製する。ステップ203において土砂2に発泡剤12を添加し、ステップ205において土砂2と膜形成剤14の水溶液とを混合する。同図では、発泡の開始を遅らせるため、ステップ202において例えば酒石酸のみを土砂2に添加すると共にステップ204において重曹を膜形成剤14に添加し、ステップ205において酒石酸及び重曹を混合している。更にステップ206において、土砂2と発泡剤12と膜形成剤14との混合物を適当な形状及び大きさ(サイズ)に成形して水酸化カルシウム水溶液等の膜化剤15中に適当な時間(例えば数分〜数百分)浸漬し、図4(A)に示すように土砂2及び発泡剤12をコーティング膜11で包んだ膜封入土砂10を形成する。膜封入土砂10の形状及び大きさは放流する水流7の状況(例えば岩の有無)、深度、流速、流量等の条件に応じて適当に選択できるが、例えば大きさを数cm〜数十cmとし、形状を球形、円筒形、三方塊形、楕円形等とすることができる。   In step 201 in FIG. 2, the earth and sand 2 are scooped up from the reservoir 1, and moisture is dried to some extent as necessary. In step 202, for example, a film forming agent 14 such as a sodium alginate aqueous solution or a CMC sodium aqueous solution is dissolved in water to prepare an aqueous solution having a required concentration. In step 203, the foaming agent 12 is added to the earth and sand 2, and in step 205, the earth and sand 2 and the aqueous solution of the film forming agent 14 are mixed. In the figure, in order to delay the start of foaming, for example, only tartaric acid is added to the earth and sand 2 in step 202, sodium bicarbonate is added to the film forming agent 14 in step 204, and tartaric acid and sodium bicarbonate are mixed in step 205. Further, in Step 206, the mixture of the earth and sand 2, the foaming agent 12 and the film forming agent 14 is formed into an appropriate shape and size (size), and is put into the film forming agent 15 such as an aqueous calcium hydroxide solution for an appropriate time (for example, (Several minutes to several hundred minutes) Immersion is performed to form a film-containing earth and sand 10 in which the earth and sand 2 and the foaming agent 12 are wrapped with the coating film 11 as shown in FIG. The shape and size of the membrane-enclosed earth and sand 10 can be appropriately selected according to the condition of the water stream 7 to be discharged (for example, presence or absence of rocks), depth, flow velocity, flow rate, etc. For example, the size is several cm to several tens of cm And the shape can be spherical, cylindrical, trigonal, elliptical, or the like.

[実験例]
図2の方法でコーティング膜11に包んだ膜封入土砂10を水流7に浮かべることができるか否かを確認するため、膜形成剤14の濃度(ステップ202参照)、土砂2に対する発泡剤12の添加量(ステップ203及び204参照)、及び土砂2に対する膜形成剤14の混合量(ステップ205参照)を変えながら、膜封入土砂10の水上浮遊の可能性を確認する実験を行った。本実験では、膜形成剤14として濃度4%、2%、及び1%の3種類のアルギン酸水溶液を用い、発泡剤12として酒石酸及び重曹を用いた。10gの土砂2に対し、酒石酸及び重曹を0.1g、0.2g、又は0.3g添加し、前記3種類の膜形成剤14の何れかを5g、10g、又は20g混合し、酒石酸及び重曹の添加量とアルギン酸水溶液の混合量とが異なる土砂試料の各々を塩化カルシウム水溶液(例えば濃度0.2M〜0.4M)に2分間浸けてコーディング膜11を形成した膜封入土砂10が水上に浮遊するか否かを確認した。また、浮遊した場合は水中に沈むまでの浮遊時間を測定した。アルギン酸水溶液の濃度別の実験結果を、膜封入土砂10が水上に浮遊した場合を○、しない場合を×として表1に示す。
[Experimental example]
In order to confirm whether or not the membrane-enclosed earth and sand 10 wrapped in the coating film 11 by the method of FIG. 2 can float on the water stream 7, the concentration of the film-forming agent 14 (see step 202), the foaming agent 12 relative to the earth and sand 2 Experiments were conducted to confirm the possibility of floating of the membrane-enclosed earth and sand 10 on the water while changing the amount added (see steps 203 and 204) and the amount of the film-forming agent 14 mixed with the earth and sand 2 (see step 205). In this experiment, three types of aqueous solutions of alginic acid having a concentration of 4%, 2%, and 1% were used as the film forming agent 14, and tartaric acid and sodium bicarbonate were used as the foaming agent 12. Add 10g of tartaric acid and sodium bicarbonate 0.1g, 0.2g, or 0.3g to 10g of earth and sand 2 and mix 5g, 10g, or 20g of any one of the three types of film formers, and add tartaric acid and sodium bicarbonate. Whether or not the membrane-enclosed earth and sand 10 in which the coding film 11 is formed by immersing each of the earth and sand samples having different mixing amounts of the aqueous solution and the alginic acid aqueous solution in a calcium chloride aqueous solution (for example, concentration 0.2M to 0.4M) for 2 minutes. confirmed. Moreover, when it floated, the floating time until it sinks in water was measured. Table 1 shows the experimental results according to the concentration of the alginate aqueous solution, where the case where the membrane-enclosed earth and sand 10 floats on the water is indicated as ◯, and the case where it is not indicated as ×.

Figure 0004067100
Figure 0004067100

表1の試料No.21〜29の実験結果から分かるように、濃度1%のアルギン酸水溶液では、コーティング膜11が薄すぎて酒石酸及び重曹から発生する気泡により直ぐに破れてしまい、土砂2を水流7に浮遊させることができなかった。また、試料No.1〜3及び試料No.11〜13の実験結果から分かるように、アルギン酸水溶液の混合量が土砂量より少ない場合は十分な強度の膜11を形成することができず、土砂2を水流7に浮遊させることができなかった。更に、表1の試料No.4〜9及び試料No.14〜19では土砂2を水流7に浮遊するコーディング膜11を形成できたが、酒石酸及び重曹の添加量が0.1gのときは膜封入土砂10の水上浮遊時間が短く、酒石酸及び重曹の添加量を0.2g、0.3gに増やすに応じて膜封入土砂10の水上浮遊時間が長くなることを確認した。酒石酸及び重曹の添加量に応じて水上浮遊時間が長くなる理由は、アルギン酸とカルシウムイオンとの反応で形成されたアルギン酸カルシウムゲル膜が多少通気性を有するため、酒石酸及び重曹の反応で生じた二酸化炭素の散逸する時間が長くなるからと考えられる。   As can be seen from the experimental results of Sample Nos. 21 to 29 in Table 1, in the aqueous solution of alginic acid having a concentration of 1%, the coating film 11 is too thin and is easily broken by bubbles generated from tartaric acid and baking soda, and the earth and sand 2 is flown through the water 7 Could not be suspended. Further, as can be seen from the experimental results of Sample Nos. 1 to 3 and Samples Nos. 11 to 13, when the amount of the alginate aqueous solution is less than the amount of earth and sand, the film 11 having sufficient strength cannot be formed, 2 could not be suspended in the water stream 7. Furthermore, in samples Nos. 4 to 9 and Nos. 14 to 19 in Table 1, the coding membrane 11 that floats the earth and sand 2 in the water stream 7 could be formed, but when the amount of tartaric acid and sodium bicarbonate added was 0.1 g, the membrane was enclosed. It was confirmed that the water floating time of the membrane-enclosed earth and sand 10 increased as the amount of tartaric acid and sodium bicarbonate added increased to 0.2 g and 0.3 g. The reason why the floating time on the water becomes longer depending on the amount of tartaric acid and sodium bicarbonate added is that the calcium alginate gel film formed by the reaction of alginic acid and calcium ions has some air permeability, so that the dioxide produced by the reaction of tartaric acid and sodium bicarbonate. This is thought to be due to the longer time for carbon to dissipate.

表1の実験結果から、濃度2%以上の膜形成剤14を土砂2に対し同量以上の割合で混合すれば、水流7に浮遊する膜11を形成できることが分かる。水流7に浮遊するコーディング膜11を経済的に形成するためには、膜形成剤14の濃度を2〜4%とし、土砂2に対する混合量を1:1〜2程度とするのが適当である。また、その膜11の気密性に応じて発泡剤12の添加量を調節することにより、膜封入土砂10の水上浮遊時間を調整できることが分かる。膜封入土砂10の水上浮遊時間を水流7の流速に応じて調節すれば、水流7による膜封入土砂10の搬送距離を予測することができる。アルギン酸水溶液・酒石酸及び重曹以外の膜形成剤14・発泡剤12を用いる場合も、表1の実験と同様にして、土砂2の浮遊時間に応じて適当な混合量・添加量を実験的に求めることができる。   From the experimental results in Table 1, it can be seen that the film 11 floating in the water stream 7 can be formed by mixing the film forming agent 14 having a concentration of 2% or more with the earth and sand 2 in the same amount or more. In order to economically form the coding film 11 floating in the water stream 7, it is appropriate that the concentration of the film forming agent 14 is 2 to 4% and the mixing amount with respect to the earth and sand 2 is about 1: 1 to 2. . It can also be seen that the floating time of the membrane-enclosed earth and sand 10 on the water can be adjusted by adjusting the amount of the foaming agent 12 added according to the airtightness of the membrane 11. If the floating time of the membrane-enclosed earth and sand 10 is adjusted according to the flow velocity of the water stream 7, the transport distance of the membrane-enclosed earth and sand 10 by the water stream 7 can be predicted. When using a film-forming agent 14 and foaming agent 12 other than alginic acid aqueous solution, tartaric acid and baking soda, as in the experiment of Table 1, the appropriate mixing amount and addition amount are experimentally determined according to the floating time of earth and sand 2. be able to.

例えば、図1の実施例において土砂2を水流7に浮遊するに十分な強度の膜11で包み、その膜11の気密性と放流位置から河口9までの予定搬送距離と水流7の流速とに応じて発泡剤12の添加量を調整することにより、膜封入土砂10を河口9まで水流7に浮かべて搬送し且つ河口9の水底に沈めることができる。河口9の水底に沈んだ膜封入土砂10は、生分解可能な材料製の膜11が徐々に崩壊して土砂2を流出し、河口9に隣接する海浜・干潟8へ土砂2を供給する。すなわち、本発明は干潟8の回復や再生に有効に利用できる。また同様にして、水流7の所要下流位置で沈むように発泡剤12を添加することにより、その下流位置に土砂2を供給することも可能である。   For example, in the embodiment of FIG. 1, the earth and sand 2 is wrapped with a film 11 having sufficient strength to float in the water stream 7, and the airtightness of the film 11, the planned transport distance from the discharge position to the estuary 9, and the flow velocity of the water stream 7 Accordingly, by adjusting the amount of the foaming agent 12 added, the membrane-filled earth and sand 10 can be floated and conveyed in the water stream 7 to the estuary 9 and submerged in the bottom of the estuary 9. The membrane-enclosed earth and sand 10 sinking to the bottom of the estuary 9 gradually collapses the membrane 11 made of a biodegradable material and flows out of the earth and sand 2 and supplies the earth and sand 2 to the beach and tidal flat 8 adjacent to the estuary 9. That is, the present invention can be effectively used for recovery and regeneration of the tidal flat 8. Similarly, it is also possible to supply the earth and sand 2 to the downstream position by adding the foaming agent 12 so as to sink at the required downstream position of the water stream 7.

また、図1に示すように、膜封入土砂10を河口9まで水流7に浮かべて搬送した上で回収し、回収した膜封入土砂10を膜溶解装置20へ投入して膜11を溶かして土砂2を取り出し、取り出した土砂2を海浜や干潟8の造成に供給することも可能である。例えばアルギン酸とカルシウムイオン溶液との反応により形成された膜11は、アルカリ溶液(水酸化ナトリウム水溶液等)に溶解する。また水溶性ビニロンフィルム製の膜11は、高温水(例えば30℃以上)に所要時間(例えば90分以上)浸けておけば溶解する。図示例の膜溶解装置20の一例は、アルカリ溶液や高温水等の膜溶解剤21(膜溶解液)を含むものである。   In addition, as shown in FIG. 1, the membrane-enclosed earth and sand 10 is floated and transported to the river mouth 9 in the water stream 7 and collected, and the collected membrane-enclosed earth and sand 10 is introduced into the membrane dissolving apparatus 20 to melt the membrane 11 and the earth and sand. It is also possible to take out 2 and supply the taken out earth and sand 2 to the creation of a beach or a tidal flat 8. For example, the film 11 formed by the reaction between alginic acid and a calcium ion solution is dissolved in an alkaline solution (such as an aqueous sodium hydroxide solution). The film 11 made of a water-soluble vinylon film dissolves when immersed in high-temperature water (for example, 30 ° C. or more) for a required time (for example, 90 minutes or more). An example of the membrane dissolving apparatus 20 in the illustrated example includes a membrane dissolving agent 21 (membrane dissolving solution) such as an alkaline solution or high-temperature water.

本発明によれば、土砂2に含まれる泥分を砂や石と共に膜11に封入し、河川等の自然な流れを利用して経済的に搬送することができ、省エネルギー的な土砂搬送が可能となる。また、土砂2に対する膜形成剤14の混合量と発泡剤12の添加量とを調節することにより、土砂2を水流7の所要下流位置まで膜11に包んだまま搬送し、所要下流位置において膜11を自然に崩壊させて土砂2を流出させるか又は膜11と共に土砂2を回収することができる。更に発泡剤12の添加量が異なる複数の膜封入土砂10を放流することにより、水流7の様々な位置で膜封入土砂10を自然に崩壊させ、その特定位置に供給することができる。   According to the present invention, mud contained in the earth and sand 2 can be enclosed in the membrane 11 together with sand and stones, and can be transported economically using natural flows such as rivers, and energy-saving earth and sand transport is possible. It becomes. Further, by adjusting the mixing amount of the film forming agent 14 with respect to the earth and sand 2 and the addition amount of the foaming agent 12, the earth and sand 2 is conveyed while being wrapped in the film 11 to the required downstream position of the water stream 7, and the film at the required downstream position. 11 can be naturally collapsed to allow the sediment 2 to flow out, or the sediment 2 can be recovered together with the membrane 11. Furthermore, by discharging a plurality of membrane-enclosed earth and sand 10 having different addition amounts of the foaming agent 12, the membrane-enclosed earth and sand 10 can be naturally collapsed at various positions in the water stream 7 and supplied to the specific position.

こうして本発明の目的である「泥分が含まれる土砂を経済的に搬送する水流浮上式搬送方法」の提供を達成できる。   Thus, it is possible to achieve the “water flow floating conveying method for economically conveying mud-containing earth and sand” which is an object of the present invention.

図3は、土砂2をコーティング膜11で包む他の方法の実施例を示す。この実施例では、図2のように土砂2と膜形成剤14とを混合するのではなく土砂2の表面にいわば衣で包むように膜形成剤14を塗布し、図4(B)に示すように膜形成剤14が塗布された土砂2を膜化剤15に浸けてコーティング膜11を形成している。土砂2と膜形成剤14とを混合する方法に比し、土砂2の表面に膜形成剤14を塗布する方法によれば、土砂2を封入するために必要な膜形成剤14の量を節約することができ、経済性が得られる。   FIG. 3 shows an embodiment of another method for wrapping earth and sand 2 with a coating film 11. In this embodiment, instead of mixing the earth and sand 2 and the film-forming agent 14 as shown in FIG. 2, the film-forming agent 14 is applied to the surface of the earth and sand 2 so as to be wrapped in clothing, as shown in FIG. 4 (B). The coating film 11 is formed by immersing the earth and sand 2 coated with the film forming agent 14 in the film forming agent 15. Compared to the method of mixing the earth and sand 2 and the film forming agent 14, the method of applying the film forming agent 14 to the surface of the earth and sand 2 saves the amount of the film forming agent 14 necessary for enclosing the earth and sand 2. Can be economical.

図3のステップ301では貯水池1から取り上げた土砂2を適当な形に成形する。土砂2が乾燥している場合は、必要に応じて適宜水を加えて成形してもよい。ステップ302において膜形成剤14の水溶液に発泡剤12を添加して発泡剤入り膜形成剤14の水溶液を調製し、例えば成形した土砂2の表面に発泡剤入り膜形成剤14の水溶液を塗布することにより、土砂2を膜形成剤14及び発泡剤12で包む。ステップ304において、表面に膜形成剤14及び発泡剤12が塗布された土砂2を膜化剤15中に浸漬することにより、図4(B)に示すように土砂2及び発泡剤12をコーティング膜11で包んだ膜封入土砂10を形成する。同図においても、土砂2の浮遊時間に応じて、膜形成剤14の適当な混合量と発泡剤12の適当な添加量とを実験的に調節することができる。   In step 301 of FIG. 3, the earth and sand 2 picked up from the reservoir 1 is formed into an appropriate shape. When the earth and sand 2 are dry, you may shape | mold by adding water suitably as needed. In step 302, the foaming agent 12 is added to the aqueous solution of the film forming agent 14 to prepare an aqueous solution of the film forming agent 14 containing the foaming agent. For example, the aqueous solution of the film forming agent 14 containing the foaming agent is applied to the surface of the molded earth and sand 2 Thus, the earth and sand 2 are wrapped with the film forming agent 14 and the foaming agent 12. In step 304, the earth and sand 2 having the surface coated with the film forming agent 14 and the foaming agent 12 are dipped in the film forming agent 15, so that the earth and sand 2 and the foaming agent 12 are coated as shown in FIG. A film enclosing earth and sand 10 wrapped with 11 is formed. Also in this figure, the appropriate mixing amount of the film forming agent 14 and the appropriate addition amount of the foaming agent 12 can be experimentally adjusted according to the floating time of the earth and sand 2.

図3の流れ図では、ステップ302において土砂2を膜形成剤14及び発泡剤12で包んだ後、その表面に更に膜形成剤14を塗布して膜化剤15中に浸けている(ステップ303)。土砂2を包むコーティング膜11の内部に発泡剤12が混入すると、発泡剤12の発泡によって膜11が破れ易くなる。ステップ303において、発泡剤12の外側に膜形成剤14を塗布した上で膜化剤15中に浸けることにより、膜11の内部への発泡剤12の混入を避け、破れ難い十分な強度のコーディング膜11を形成することが期待できる。但し、膜形成剤14及び発泡剤12を表面に塗布したステップ302の状態で十分な強度の膜11が形成できる場合は、ステップ303は省略可能である。   In the flowchart of FIG. 3, after the earth and sand 2 are wrapped in the film forming agent 14 and the foaming agent 12 in step 302, the film forming agent 14 is further applied to the surface and immersed in the film forming agent 15 (step 303). . When the foaming agent 12 is mixed into the coating film 11 that encloses the earth and sand 2, the film 11 is easily broken by foaming of the foaming agent 12. In step 303, the film forming agent 14 is applied to the outside of the foaming agent 12, and then immersed in the filming agent 15. Thus, the foaming agent 12 is prevented from being mixed into the inside of the film 11, and the coating has sufficient strength and is not easily broken. Formation of the film 11 can be expected. However, if the film 11 having sufficient strength can be formed in the state of step 302 in which the film forming agent 14 and the foaming agent 12 are applied to the surface, step 303 can be omitted.

本発明の一実施例の説明図である。It is explanatory drawing of one Example of this invention. 膜形成剤及び膜化剤を用いて土砂封入膜を形成する一例の説明図である。It is explanatory drawing of an example which forms an earth-and-sand enclosure film | membrane using a film forming agent and a film forming agent. 膜形成剤及び膜化剤を用いて土砂封入膜を形成する他の一例の説明図である。It is explanatory drawing of another example which forms an earth-and-sand enclosure film | membrane using a film forming agent and a film forming agent. 図2及び図3の方法により形成した膜封入土砂の図式的断面図である。FIG. 4 is a schematic cross-sectional view of a membrane-sealed earth and sand formed by the method of FIGS. 2 and 3.

符号の説明Explanation of symbols

1…ダム貯水池 2…土砂
4…土砂採取装置
5…添加装置 6…コーティング装置
7…水流 8…海浜・干潟
9…河口 10…膜封入土砂
11…膜 12…発泡剤
13…気泡 14…膜形成剤
15…膜化剤
20…膜溶解装置 21…膜溶解剤
DESCRIPTION OF SYMBOLS 1 ... Dam reservoir 2 ... Sediment 4 ... Sediment collection device 5 ... Additive device 6 ... Coating device 7 ... Water flow 8 ... Beach and tidal flat 9 ... Estuary 10 ... Membrane-containing sediment
11 ... Membrane 12 ... Foaming agent
13 ... Bubbles 14 ... Film-forming agent
15 ... Filming agent
20 ... Membrane dissolving device 21 ... Membrane dissolving agent

Claims (7)

土砂を発泡剤と共に膜に封入し、前記発泡剤から発生する気泡により土砂を水流に浮かべて搬送してなる土砂の水流浮上式搬送方法。 A water-floating transport method for earth and sand, wherein earth and sand are enclosed in a film together with a foaming agent , and the earth and sand are floated and transported by air bubbles generated from the foaming agent . 請求項1の搬送方法において、前記発泡剤の量を、前記土砂の搬送予定距離と前記水流の流速と前記膜の気密性とに応じて調整してなる土砂の水流浮上式搬送方法。 2. The method according to claim 1, wherein the amount of the foaming agent is adjusted in accordance with a planned transport distance of the earth and sand, a flow velocity of the water stream, and an airtightness of the film. 請求項1又は2の搬送方法において、前記発泡剤の量を、前記土砂が予定距離だけ搬送されたのち前記膜と共に水底へ沈むように調整してなる土砂の水流浮上式搬送方法。 The method according to claim 1 or 2 , wherein the amount of the foaming agent is adjusted such that the amount of the foaming agent is adjusted to sink to the bottom of the water together with the membrane after the earth and sand are conveyed by a predetermined distance. 請求項1又は2の搬送方法において、予定距離だけ搬送した土砂を前記膜と共に水流から回収し、膜溶解剤により前記膜を溶かして土砂を取り出してなる土砂の水流浮上式搬送方法。 The method according to claim 1 or 2 , wherein the earth and sand transported for a predetermined distance are collected from the water flow together with the film, and the film is melted with a film dissolving agent to remove the earth and sand. 請求項1から4の何れかの搬送方法において、前記膜を生分解可能な材料製としてなる土砂の水流浮上式搬送方法。 5. The method according to claim 1 , wherein the membrane is made of a material capable of biodegradation. 請求項の搬送方法において、前記土砂に膜化剤との反応により膜を形成する膜形成剤を混合又は塗布し、前記膜形成剤が混合又は塗布された土砂を前記膜化剤に浸すことにより前記膜で封入してなる土砂の水流浮上式搬送方法。 6. The conveying method according to claim 5 , wherein a film forming agent that forms a film by reaction with a film forming agent is mixed or applied to the earth and sand, and the earth or sand to which the film forming agent is mixed or applied is immersed in the film forming agent. A method of conveying the earth and sand entrained by the membrane according to the above method. 請求項の搬送方法において、前記膜形成剤をアルギン酸、カルボキシメチルセルロース又はペクチン溶液とし、前記膜化剤をカルシウムイオン溶液としてなる土砂の水流浮上式搬送方法。 The method according to claim 6 , wherein the film-forming agent is alginic acid, carboxymethylcellulose, or a pectin solution, and the film-forming agent is a calcium ion solution.
JP2003291994A 2003-08-12 2003-08-12 Sediment flow method Expired - Fee Related JP4067100B2 (en)

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