JP5723569B2 - Sediment throwing method and sand throwing device using treme tube - Google Patents

Sediment throwing method and sand throwing device using treme tube Download PDF

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JP5723569B2
JP5723569B2 JP2010236895A JP2010236895A JP5723569B2 JP 5723569 B2 JP5723569 B2 JP 5723569B2 JP 2010236895 A JP2010236895 A JP 2010236895A JP 2010236895 A JP2010236895 A JP 2010236895A JP 5723569 B2 JP5723569 B2 JP 5723569B2
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pipe
sand
tremy
earth
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JP2012087581A (en
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宗男 津田
宗男 津田
信彦 松田
信彦 松田
将英 竹田
将英 竹田
五十嵐 学
学 五十嵐
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Toa Corp
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本発明は、トレミー管を用いた土砂の投入方法および土砂の投入装置に関し、さらに詳しくは、投入土砂によるトレミー管の閉塞を防止しつつ、汚濁の拡散を抑制できるトレミー管を用いた土砂の投入方法および土砂の投入装置に関するものである。   TECHNICAL FIELD The present invention relates to a method and apparatus for depositing earth and sand using a tremy pipe, and more particularly, to throwing earth and sand using a tremy pipe that can prevent the diffusion of pollution while preventing the tremmy pipe from being blocked by the loaded earth and sand. The present invention relates to a method and an apparatus for introducing earth and sand.

海等の水底に土砂を投入する際に、トレミー管を用いる方法が知られている(例えば、特許文献1の第1図〜第4図)。トレミー管を通じて海底に土砂を投入する際には、管内で土砂が詰まって閉塞しないように、例えば、海面近傍(水深1m〜2m程度)からくみ上げた海水をトレミー管の上端から注入するようにしている。また、投入土砂により生じる汚濁の拡散を抑制するために、種々の提案がなされている。特許文献1では、トレミー管の下端の撒布口の周囲に濁水吸入口を設け、発生した濁水を濁水吸入口から吸入してトレミー管内に中途からノズルで噴出するようにしている(第5図〜第8図等参照)。   A method of using a tremy tube when putting earth and sand into a water bottom such as the sea is known (for example, FIG. 1 to FIG. 4 of Patent Document 1). When throwing earth and sand into the seabed through the tremy pipe, in order to prevent clogging and blockage in the pipe, for example, sea water pumped up from the vicinity of the sea surface (water depth of about 1m to 2m) is injected from the upper end of the tremy pipe. Yes. In addition, various proposals have been made in order to suppress the diffusion of pollution caused by the input soil. In Patent Document 1, a muddy water suction port is provided around the spray port at the lower end of the tremy tube, and the generated muddy water is sucked from the muddy water suction port and ejected from the middle through the nozzle (FIG. 5 to FIG. 5). (See FIG. 8 etc.)

ところで、水底の窪地に土砂を投入して埋め戻す際に、夏季よりも秋季に、汚濁が拡散し易いことが報告されている。そこで、本願発明者らは、この現象に注目し、汚濁拡散に対する水域の水の密度の影響を分析した。この分析で得た知見に基づいて、種々検討を重ねることにより、投入土砂によるトレミー管の閉塞を防止しつつ、投入土砂により生じる汚濁の拡散を抑制する手法を創作するに至った。   By the way, it has been reported that when sand and sand are put back into a depression in the bottom of the water, pollution is more likely to diffuse in the autumn than in the summer. Therefore, the inventors of the present application focused on this phenomenon and analyzed the influence of the water density in the water area on the pollution diffusion. Based on the knowledge gained from this analysis, various studies have been made to create a technique for preventing the diffusion of pollution caused by the input soil while preventing the tremmy tube from being blocked by the input soil.

特開昭56−119035号公報JP 56-1119035 A

本発明の目的は、投入土砂によるトレミー管の閉塞を防止しつつ、汚濁の拡散を抑制できるトレミー管を用いた土砂の投入方法および土砂の投入装置を提供することにある。   An object of the present invention is to provide an earth and sand charging method and an earth and sand charging apparatus using a tremy pipe that can suppress the diffusion of pollution while preventing the tremy pipe from being blocked by the charged earth and sand.

上記目的を達成するため本発明のトレミー管を用いた土砂の投入方法は、土砂を投入する現場において、トレミー管の外側の位置にこのトレミー管と離してこのトレミー管の上方まで延びる吸入管を配置し、前記トレミー管の外側の位置に設置した前記吸入管の下端からこの吸入管を通じて、この現場の水深の50%の水深よりも深い位置から水をくみ上げて、この現場の50%の水深に存在する水よりも密度の高い水を、前記トレミー管の上端から注入しつつ、前記トレミー管を通じて土砂を水深5m〜30mの水底に投入することにより、投入した土砂によって生じる汚濁の拡散を抑制することを特徴とする。 In order to achieve the above-mentioned object, the earth and sand throwing method using the tremy pipe of the present invention includes a suction pipe extending to the upper side of the tremy pipe at a position outside the tremy pipe at a site where the earth and sand are poured. The water is pumped up from a position deeper than 50% of the water depth of the site through the suction pipe from the lower end of the suction tube installed at a position outside the tremy tube, and the water depth of 50% of the site is water dense than water present in, while injecting from the upper end of the tremie tube, by injecting sediment into the sea bed in water depths 5m~30m through the tremie pipe, suppress the diffusion of contamination caused by the charged sediment It is characterized by doing.

本発明の土砂の投入装置は、土砂を投入する水深5m〜30mの現場の水底近傍から水上に立設されるトレミー管と、この現場の水深の50%の水深に存在する水よりも密度の高い水を、トレミー管の上端から注入させる注水手段とを備え、前記注水手段が、前記トレミー管の外側の位置でこのトレミー管と離れて配置されて前記現場の水深の50%の水深よりも深い位置から前記トレミー管の上方まで延びる吸入管と、この吸入管に接続される吸入ポンプとにより構成され、前記密度の高い水が吸入される前記吸入管の下端が前記トレミー管の外側の位置に設置されて、前記吸入管の下端からこの吸入管を通じて、この現場の水深の50%の水深よりも深い位置から水をくみ上げて、この現場の50%の水深に存在する水よりも密度の高い水を、前記トレミー管の上端から注入しつつ、前記トレミー管を通じて土砂を水深5m〜30mの水底に投入することにより、投入した土砂によって生じる汚濁の拡散を抑制する構成にしたことを特徴とする。 The earth and sand injection device of the present invention has a density higher than that of water existing at a water depth of 50% of the water depth of this site and a tremy pipe standing on the water from the vicinity of the bottom of the site where the water depth is 5 to 30 m. Water injection means for injecting high water from the upper end of the tremmy pipe, and the water injection means is disposed away from the tremy pipe at a position outside the tremy pipe so that the water depth is more than 50% of the water depth of the site. A suction pipe extending from a deep position to above the tremy pipe and a suction pump connected to the suction pipe, and a lower end of the suction pipe through which the high-density water is sucked is located outside the tremy pipe. The water is pumped from the lower end of the suction pipe through the suction pipe from a position deeper than the depth of 50% of the water depth of the site, and has a density higher than that of water existing at the depth of 50% of the depth of the site. high , Said while injecting from the upper end of the tremie tube, by injecting sediment into the sea bed in water depths 5m~30m through the tremie pipe, characterized in that the inhibiting arrangement the diffusion of contamination caused by the charged sediment.

本発明によれば、トレミー管の上端から水を注入しつつ、土砂を投入することにより、トレミー管内での土砂の閉塞を防止することができる。しかも、土砂を投入する現場の水面近傍に存在する水よりも密度の高い水を使用するので、水面近傍の水を使用した場合に比して水の密度が高いことが作用して、土砂投入した際に汚濁が拡散し難くなる。   ADVANTAGE OF THE INVENTION According to this invention, blockage | closure of the earth and sand in a tremy pipe | tube can be prevented by throwing in earth and sand, injecting water from the upper end of a treme pipe | tube. Moreover, since water with a higher density than the water existing near the water surface at the site where soil is introduced is used, the water density is higher than when water near the water surface is used. When it is done, the pollution becomes difficult to diffuse.

本発明の土砂の投入方法では、前記現場において、この現場の水深の50%の水深よりも深い位置から水をくみ上げ、この水をトレミー管の上端から注入する。本発明の土砂の投入装置では、前記注水手段が、前記トレミー管の外側の位置でこのトレミー管と離れて配置され、前記現場の水深の50%の水深よりも深い位置から前記トレミー管の上方まで延びる吸入管と、この吸入管に接続される吸入ポンプとにより構成される。これにより、土砂を投入する現場の水面近傍に存在する水よりも密度の高い水を、容易に確保することができる。 In the earth and sand injection method of the present invention, water is drawn up from a position deeper than 50% of the water depth at the site, and the water is injected from the upper end of the tremy tube. In the earth and sand injection device of the present invention, the water injection means is disposed away from the tremy pipe at a position outside the tremy pipe, and is located above the tremy pipe from a position deeper than 50% of the water depth of the site water. And a suction pump connected to the suction pipe. Thereby, the water whose density is higher than the water which exists in the vicinity of the water surface of the field where earth and sand are thrown in can be secured easily.

本発明の土砂の投入装置の実施形態を例示する説明図である。It is explanatory drawing which illustrates embodiment of the earth and sand injection | throwing-in apparatus of this invention. 土砂の投入装置の参考形態を例示する説明図である。It is explanatory drawing which illustrates the reference form of the earth and sand injection | throwing-in apparatus. 実験装置を示す説明図である。It is explanatory drawing which shows an experimental apparatus. 実施例1の汚濁拡散状態を数値計算に基づいて示した説明図である。It is explanatory drawing which showed the pollution diffusion state of Example 1 based on numerical calculation. 実施例2の汚濁拡散状態を数値計算に基づいて示した説明図である。It is explanatory drawing which showed the pollution diffusion state of Example 2 based on numerical calculation. 比較例1の汚濁拡散状態を数値計算に基づいて示した説明図である。It is explanatory drawing which showed the pollution diffusion state of the comparative example 1 based on numerical calculation. 比較例2の汚濁拡散状態を数値計算に基づいて示した説明図である。It is explanatory drawing which showed the pollution diffusion state of the comparative example 2 based on numerical calculation.

以下、本発明のトレミー管を用いた土砂の投入方法およびその装置を図に示した実施形態に基づいて説明する。   DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, a method and apparatus for introducing earth and sand using a tremy tube of the present invention will be described based on the embodiments shown in the drawings.

図1に例示するように本発明の土砂の投入装置1は、トレミー管2と、トレミー管2の上端から水Wをトレミー管2内に流入させる吸入管4および吸入ポンプ5で構成される注水手段とを備えている。   As illustrated in FIG. 1, the earth and sand injection device 1 according to the present invention includes a tremely pipe 2, and a water injection system including a suction pipe 4 and a suction pump 5 that allow water W to flow into the tremy pipe 2 from the upper end of the tremy pipe 2. Means.

トレミー管2は、作業船9に設けられた保持部材7によって保持されて、土砂Sを投入する現場の水底近傍から水上に立設される。トレミー管2の上端にはホッパ3が設置されている。トレミー管2の大きさは、例えば、内径が1m〜5m程度、全長が7m〜25m程度、肉厚が10mm〜15mm程度である。   The tremy pipe 2 is held by a holding member 7 provided on the work boat 9 and is erected on the water from the vicinity of the water bottom at the site where the earth and sand S is introduced. A hopper 3 is installed at the upper end of the tremy tube 2. The size of the tremy tube 2 is, for example, an inner diameter of about 1 m to 5 m, a total length of about 7 m to 25 m, and a wall thickness of about 10 mm to 15 mm.

この実施形態では、トレミー管2は、ストレートな円筒鋼管を用いているが、ストレート形状に限らず、下方がより拡径した形状等を用いることができる。また、トレミー管2は、伸縮タイプ、非伸縮タイプの両方を用いることができる。伸縮タイプの場合は、例えば、複数の管体をテレスコピック状に連結した構造にする。非伸縮タイプの場合は、単純な一本管、或いは、複数の管体を継ぎ足した構造にする。トレミー管2は単管に限らず、内管と外管とで構成される二重管を用いることもできる。   In this embodiment, the tremy tube 2 is a straight cylindrical steel tube, but is not limited to a straight shape, and may have a shape in which the lower diameter is further expanded. Moreover, the tremey tube 2 can use both an expansion-contraction type and a non-expansion type. In the case of the expansion / contraction type, for example, a structure in which a plurality of tubular bodies are connected in a telescopic manner is used. In the case of the non-expandable type, a simple single pipe or a structure in which a plurality of pipes are added is used. The tremy tube 2 is not limited to a single tube, and a double tube composed of an inner tube and an outer tube can also be used.

吸入管4の下端は現場の水面近傍よりも深くて水底に接しない位置に配置されている。本願発明の水面近傍とは、水面から1〜2m程度の位置である。具体的には、吸入管4の下端は水深Hの50%の水深h(=H×50%)よりも深くて水底に接しない位置に配置され、上端はホッパ3の上部開口に配置されている。このように吸入管4は、所定の水深位置からトレミー管2の上方まで延設されている。吸入ポンプ5は作業船9の船上に設置され、吸入管4の中途に設けられている。吸入管4は例えば、樹脂製の可撓性のあるパイプ等を用いる。 The lower end of the suction pipe 4 is disposed at a position deeper than the vicinity of the water surface at the site and not in contact with the water bottom. The vicinity of the water surface of the present invention is a position of about 1 to 2 m from the water surface. Specifically, the lower end of the suction pipe 4 is disposed at a position that is deeper than the water depth h (= H × 50% ) 50% of the water depth H and does not contact the water bottom, and the upper end is disposed at the upper opening of the hopper 3. Yes. Thus, the suction pipe 4 is extended from the predetermined water depth position to the upper part of the tremy pipe 2. The suction pump 5 is installed on the work boat 9 and is provided in the middle of the suction pipe 4. As the suction pipe 4, for example, a flexible pipe made of resin is used.

ホッパ3に隣接して土砂投入手段となるコンベヤベルト8が設置されている。コンベヤベルト8はホッパ3を通じて、作業船9に積載された土砂Sをトレミー管2に投入する。土砂投入手段としてはその他に、バックホウのバケット等を用いることができる。   A conveyor belt 8 is installed adjacent to the hopper 3 and serves as earth and sand charging means. The conveyor belt 8 puts the earth and sand S loaded on the work ship 9 through the hopper 3 into the tremy pipe 2. In addition, a backhoe bucket or the like can be used as the earth and sand charging means.

この土砂の投入装置1を用いて水底に土砂Sを投入する方法は以下の手順となる。   The method of throwing earth and sand S into the bottom of the water using the earth and sand throwing device 1 is as follows.

まず、コンベヤベルト8を用いて、土砂Sをホッパ3に投入する。この際に、吸入ポンプ5を稼働させて吸入管4を通じてホッパ3に水Wを注入する。即ち、注水手段によって、土砂Sを投入する現場の水面近傍に存在する水よりも密度の高い水Wを、トレミー管2の上端から管内に注入する。このようにして、高い密度の水W(水底に存在する水との密度差が小さい水W)を、トレミー管2の上端から注入しつつ、トレミー管2を通じて所定量の土砂Sを水底に投入する。海での施工では、現場の海面近傍に存在する海水よりも塩分濃度が高い水Wを、トレミー管2の中に注入しつつ土砂Sを水底に投入する。   First, the earth and sand S are put into the hopper 3 using the conveyor belt 8. At this time, the suction pump 5 is operated to inject water W into the hopper 3 through the suction pipe 4. That is, water W having a higher density than water existing in the vicinity of the water surface at the site where the earth and sand S is introduced is injected into the pipe from the upper end of the tremy pipe 2 by the water injection means. In this way, a high amount of water W (water W having a small density difference from the water present at the bottom of the water) is injected from the upper end of the tremy tube 2 and a predetermined amount of earth and sand S is introduced into the bottom of the water through the tremy tube 2. To do. In the construction at sea, the earth and sand S is thrown into the bottom of the water while injecting water W having a higher salinity than seawater present near the sea surface at the site into the tremy pipe 2.

トレミー管2の中には水Wを注入しているので、粘性が高い土砂Sの場合は、この水Wによって、トレミー管2の内壁に土砂Sが付着することが防止される。また、一度に投入される土砂Sの量が過大であっても、この水Wによって、土砂Sの流れがトレミー管2の内壁との摩擦に妨げられることなく円滑になる。それ故、水Wの注入によって土砂Sがトレミー管2の中で詰まり難くなり、トレミー管2の閉塞を防止できる。   Since the water W is injected into the tremy pipe 2, in the case of the earth and sand S having a high viscosity, the water W prevents the earth and sand S from adhering to the inner wall of the tremy pipe 2. Moreover, even if the amount of the earth and sand S to be charged at one time is excessive, the flow of the earth and sand S is smoothed by the water W without being disturbed by friction with the inner wall of the tremy pipe 2. Therefore, the injection of the water W makes it difficult for the earth and sand S to be clogged in the tremy tube 2, thereby preventing the tremmy tube 2 from being blocked.

さらに、トレミー管2に注入する水Wは、水面近傍の水と比較して高密度であり、水底の水との密度差が小さい。それ故、この水Wとともに投入される土砂Sは、トレミー管2の下端から開放されても水中を浮遊し難くなり、汚濁の拡散が抑制される。特に、上方への汚濁の拡がりは小さくなる。密度の高い水を使用するほど、汚濁の拡散を抑制するには有利になる。   Furthermore, the water W to be injected into the tremy tube 2 has a higher density than the water near the water surface, and the density difference from the water at the bottom is small. Therefore, even if the earth and sand S introduced with the water W is released from the lower end of the tremy pipe 2, it becomes difficult to float in the water, and the diffusion of pollution is suppressed. In particular, the upward spread of pollution is reduced. The higher the density of water, the more advantageous it is to suppress the diffusion of pollution.

海では水深が深い程、海水の密度(塩分濃度)が高い傾向にある。また、夏季など、水温が高くなるほど水深方向で水の密度差が大きくなる。そこで、トレミー管2の管内に注入する水Wの密度を、土砂Sを投入する水底に存在する水の密度に近づけるために、吸入管4の下端は、水深Hの50%、より好ましくは70%、さらに好ましくは90%よりも深い位置に配置するIn the sea, the deeper the water, the higher the density of the seawater (salt concentration). In addition, the difference in water density in the depth direction increases as the water temperature increases, such as in summer. Therefore, in order to make the density of the water W injected into the pipe of the tremy pipe 2 close to the density of the water existing in the bottom of the water into which the earth and sand S is introduced, the lower end of the suction pipe 4 is 50% of the water depth H , more preferably 70. %, more preferably disposed at a position deeper than 90%.

このように吸入管4を配置することで、水底に存在する水との密度差がより小さい水Wを、トレミー管2の中に注入することができる。即ち、海での施工では、水底に存在する海水との塩分濃度差がより小さい水Wをトレミー管2の中に注入できる。これにより、投入した土砂Sによる汚濁の拡散を一段と抑制することが可能になる。   By disposing the suction pipe 4 in this way, water W having a smaller density difference from the water present at the bottom of the water can be injected into the tremy pipe 2. That is, in construction at sea, water W having a smaller salinity difference from seawater existing at the bottom of the water can be injected into the tremy tube 2. Thereby, it becomes possible to further suppress the diffusion of the contamination due to the introduced earth and sand S.

現場の水深Hに存在する水よりも密度が過大である水を使用すると、生態系などに悪影響が生じるおそれがある。そのため、理想的には、土砂Sを投入する水底に存在する水と同じ密度の水Wを、トレミー管2の上端から管内に注入する。   If water having a density higher than the water existing at the depth H at the site is used, there is a risk that the ecosystem will be adversely affected. Therefore, ideally, the water W having the same density as the water existing at the bottom of the earth and sand S is poured from the upper end of the tremy pipe 2 into the pipe.

図2に例示する土砂投入装置1の参考形態は、先の実施形態の注水手段のみを変更したものである。この注水手段は、吸入管4、吸入ポンプ5および貯留タンク6により構成されている。吸入管4の一端は貯留タンク6の内部に配置され、他端はホッパ3の上端開口に配置されている。貯留タンク6の設置場所は船内に限らず、船上にすることもできる。 The reference form of the earth and sand throwing-in apparatus 1 illustrated in FIG. 2 is obtained by changing only the water injection means of the previous embodiment. This water injection means is constituted by a suction pipe 4, a suction pump 5 and a storage tank 6. One end of the suction pipe 4 is disposed inside the storage tank 6, and the other end is disposed in the upper end opening of the hopper 3. The installation location of the storage tank 6 is not limited to the inside of the ship but can be on the ship.

貯留タンク6には、土砂Sを投入する現場の水面近傍に存在する水よりも密度の高い水Wが貯留されている。この参考形態の場合、土砂Sを投入する現場の水面近傍に存在する水の密度を予め把握しておき、その密度よりも高い密度の水Wを貯留タンク6に貯留する。そして、貯留タンク6に貯留した水Wを、吸入管4を通じてトレミー管2の上端から管内に注入しつつ、トレミー管2を通じて土砂Sを水底に投入する。 The storage tank 6 stores water W having a higher density than water existing in the vicinity of the water surface at the site where the earth and sand S is introduced. In the case of this reference form, the density of water existing in the vicinity of the water surface at the site where the earth and sand S is introduced is grasped in advance, and water W having a density higher than that density is stored in the storage tank 6. Then, the water S stored in the storage tank 6 is injected into the pipe from the upper end of the tremy pipe 2 through the suction pipe 4, and the earth and sand S is poured into the water bottom through the tremy pipe 2.

この参考形態では、土砂Sを投入する現場の水深Hに存在する水よりも高密度の水Wを、トレミー管2の中に注入することも可能になる。即ち、海での施工では、その水深Hに存在する海水よりも塩分濃度の高い水Wを利用することもできる。 In this reference form, it becomes possible to inject water W having a higher density than the water existing at the depth H of the site where the earth and sand S is introduced into the tremy tube 2. That is, in construction at sea, water W having a higher salinity concentration than seawater existing at the depth H can be used.

水深Hの50%、より好ましくは70%、さらに好ましくは90%の水深に存在する水よりも密度の高い水Wを貯留タンク6に貯留して、上述した実施形態と同様に、土砂Sを投入する水底に存在する水との密度差がより小さい水Wを、トレミー管2の管内に注入できる構成にする。 Water W having a higher density than water existing at a water depth of 50% , more preferably 70%, and even more preferably 90% of the water depth H is stored in the storage tank 6, and the earth and sand S is stored in the same manner as in the above-described embodiment. The water W having a smaller density difference from the water present at the bottom of the water to be introduced is configured to be injected into the tube of the tremy tube 2.

本発明は水深Hが5m〜30mの場合に適用することができる。また、海での施工に限らず河川湖沼などでの施工にも適用することができる。 The present invention can be applied when the water depth H is 5 m to 30 m. In addition, it can be applied not only to construction at sea but also to construction in rivers and lakes.

図3に示す上下2層(上層ULと下層DL)の密度構造を模擬できる実験装置10を用いて水理実験を行なった。実験装置10は、水を収容した水槽12に立設する鉛直管11を有し、鉛直管11の上端には、開閉バルブ14を介してリザーブタンク13が接続されている。そして、リザーブタンク13の濁水MWを水槽12の底面に投入し、汚濁の拡散状態を確認した。実験条件は表1に示すように、水槽12に収容した水の成層の有無と濁水MWの溶媒密度のみを異ならせて、4種類(実施例1および2、比較例1および2)について実験を行なった。   A hydraulic experiment was conducted using an experimental apparatus 10 that can simulate the density structure of the upper and lower two layers (upper layer UL and lower layer DL) shown in FIG. The experimental apparatus 10 has a vertical pipe 11 standing on a water tank 12 containing water, and a reserve tank 13 is connected to an upper end of the vertical pipe 11 via an open / close valve 14. And the muddy water MW of the reserve tank 13 was thrown into the bottom face of the water tank 12, and the diffusion state of pollution was confirmed. As shown in Table 1, the experiment conditions were varied for the four types (Examples 1 and 2 and Comparative Examples 1 and 2) with only the presence or absence of stratification of the water stored in the water tank 12 and the solvent density of the turbid water MW. I did it.

水槽12は一辺が300mmの直方体であり、鉛直管11は、トレミー管を模擬したものであり、サイズが長さ300mm、内径24mm、図3に示すように下端を水槽12の底面から50mm上方に位置するように配置した。密度成層の最大密度差は、2kg/m3とし、実験中の水温変化は微小なものとして、塩分で水槽12に収容した水の密度を調整した。また、土砂を水槽12内の水に直接投入すると、微妙な条件の違いによって濁りの発生量が大きく変化するため、実験の再現性が高い濁水MWを投入することにした。濁りの粒子にはカオリン(最大粒径0.0750mm、粘土分77.6%、シルト分22.4%、土粒子密度ρ=2690kg/m3)を使用し、その溶媒には水槽12内の水と同じものを用いて密度1010kg/m3を作成した。 The water tank 12 is a rectangular parallelepiped having a side of 300 mm, and the vertical pipe 11 is a model of a tremmy pipe. The size is 300 mm long, the inner diameter is 24 mm, and the lower end is 50 mm above the bottom of the water tank 12 as shown in FIG. Arranged to be located. The maximum density difference in the density stratification was 2 kg / m 3, and the water temperature change during the experiment was minute, and the density of the water stored in the water tank 12 was adjusted with salinity. Moreover, since the amount of turbidity generated varies greatly depending on subtle conditions when earth and sand are directly introduced into the water in the water tank 12, the turbid water MW with high reproducibility of the experiment is introduced. Kaolin (maximum particle size 0.0750 mm, clay content 77.6%, silt content 22.4%, soil particle density ρ = 2690 kg / m 3 ) is used for the turbid particles, and the solvent in the water tank 12 is used as the solvent. A density of 1010 kg / m 3 was prepared using the same water.

実験は、開閉バルブ14を瞬時に開放することにより、4秒間で100cm3の濁水MWを連続的に投入した。濁水投入から38分50秒後(実験では300秒後に相当)の汚濁の拡散状態を図4〜7に示す。尚、図4〜図7は数値計算に基づいて汚濁の拡散状態を示したものであるが、実験結果と整合していることを確認しているので、実験結果として見做せるデータである。図4〜図7では色の濃い部分ほど濁水MWが多く分布していることを示している。 In the experiment, 100 cm 3 of turbid water MW was continuously added in 4 seconds by opening the on-off valve 14 instantaneously. FIGS. 4 to 7 show the diffusion state of the contamination 38 minutes and 50 seconds after the turbid water is charged (corresponding to 300 seconds in the experiment). 4 to 7 show the diffusion state of the contamination based on numerical calculation, but since it is confirmed that it is consistent with the experimental result, the data can be regarded as the experimental result. 4 to 7 show that the darker the color, the more muddy water MW is distributed.

実施例1および2、比較例1および2のすべて場合において、濁水投入初期には水槽12の底面を這うように濁りが拡がった。その後、実施例1、2では図4および図5に示すように、汚濁の拡散は底面に限定された。一方、比較例1および2では図6および図7に示すように、時間の経過とともに汚濁が徐々に上方にも拡散した。これらの結果により、濁水の溶媒と投入地点の水塊との密度差によって汚濁の拡散状態が異なり、密度差の小さい溶媒を用いた実施例1および2では、汚濁の拡散を抑制できることが分かる。   In all cases of Examples 1 and 2 and Comparative Examples 1 and 2, the turbidity spread so as to crawl the bottom surface of the water tank 12 at the beginning of the turbid water injection. Thereafter, in Examples 1 and 2, as shown in FIGS. 4 and 5, the diffusion of the contamination was limited to the bottom surface. On the other hand, in Comparative Examples 1 and 2, as shown in FIGS. 6 and 7, the contamination gradually diffused upward as time passed. From these results, it can be seen that the diffusion state of the pollution differs depending on the density difference between the solvent of the turbid water and the water mass at the charging point, and the diffusion of the pollution can be suppressed in Examples 1 and 2 using the solvent having a small density difference.

1 投入装置
2 トレミー管
2a 保持部材
3 ホッパ
4 吸入管
5 吸入ポンプ
6 貯留タンク
7 流入管
8 コンベヤベルト
9 作業船
10 実験装置
11 鉛直管
12 水槽
13 リザーブタンク
14 開閉バルブ
S 土砂
W 水
MW 濁水
UL 上層
DL 下層
DESCRIPTION OF SYMBOLS 1 Input device 2 Tremy pipe 2a Holding member 3 Hopper 4 Suction pipe 5 Suction pump 6 Storage tank 7 Inflow pipe 8 Conveyor belt 9 Work ship 10 Experimental apparatus 11 Vertical pipe 12 Water tank 13 Reserve tank 14 Opening and shutting valve S Earth and sand W Water MW Turbid water UL Upper DL Lower layer

Claims (2)

土砂を投入する現場において、トレミー管の外側の位置にこのトレミー管と離してこのトレミー管の上方まで延びる吸入管を配置し、前記トレミー管の外側の位置に設置した前記吸入管の下端からこの吸入管を通じて、この現場の水深の50%の水深よりも深い位置から水をくみ上げて、この現場の50%の水深に存在する水よりも密度の高い水を、前記トレミー管の上端から注入しつつ、前記トレミー管を通じて土砂を水深5m〜30mの水底に投入することにより、投入した土砂によって生じる汚濁の拡散を抑制することを特徴とするトレミー管を用いた土砂の投入方法。 At the site where the earth and sand are thrown in , a suction pipe that extends to the upper side of the tremy pipe is arranged at a position outside of the tremy pipe, and the lower end of the suction pipe installed at a position outside the tremy pipe. through the suction pipe, and pumped water from deeper than 50 percent of the depth of the water depth of the field, the high water density than water present in 50% of the depth of the site, is injected from the upper end of the tremie tube On the other hand, a method for introducing earth and sand using a tremy pipe, wherein the earth and sand are introduced into the bottom of the water at a depth of 5 to 30 m through the tremy pipe to suppress the diffusion of pollution caused by the introduced earth and sand. 土砂を投入する水深5m〜30mの現場の水底近傍から水上に立設されるトレミー管と、この現場の水深の50%の水深に存在する水よりも密度の高い水を、トレミー管の上端から注入させる注水手段とを備え、前記注水手段が、前記トレミー管の外側の位置でこのトレミー管と離れて配置されて前記現場の水深の50%の水深よりも深い位置から前記トレミー管の上方まで延びる吸入管と、この吸入管に接続される吸入ポンプとにより構成され、前記密度の高い水が吸入される前記吸入管の下端が前記トレミー管の外側の位置に設置されて、前記吸入管の下端からこの吸入管を通じて、この現場の水深の50%の水深よりも深い位置から水をくみ上げて、この現場の50%の水深に存在する水よりも密度の高い水を、前記トレミー管の上端から注入しつつ、前記トレミー管を通じて土砂を水深5m〜30mの水底に投入することにより、投入した土砂によって生じる汚濁の拡散を抑制する構成にしたことを特徴とする土砂の投入装置。 From the top of the Tremy pipe, the Tremy pipe standing on the water from near the bottom of the 5 to 30 m depth where the earth and sand is thrown in, and the water having a higher density than the water existing at 50% of the water depth of the spot. Water injection means for injecting, and the water injection means is arranged at a position outside the tremy pipe and spaced apart from the tremy pipe and from a position deeper than 50% of the water depth of the site to above the tremy pipe The suction pipe is formed by an extending suction pipe and a suction pump connected to the suction pipe, and a lower end of the suction pipe through which the high-density water is sucked is installed at a position outside the tremy pipe. Water is drawn from a position deeper than 50% of the water depth of the site through the suction pipe from the lower end, and water having a higher density than water existing at the depth of 50% of the site is drawn into the upper end of the tremy pipe. While al injected by injecting sediment into the sea bed in water depths 5m~30m through the tremie pipe, dosing device sediment, characterized in that the inhibiting arrangement the diffusion of contamination caused by the charged sediment.
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