JP5085866B2 - Bag for dehydration of hydrous soil - Google Patents
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- JP5085866B2 JP5085866B2 JP2005378304A JP2005378304A JP5085866B2 JP 5085866 B2 JP5085866 B2 JP 5085866B2 JP 2005378304 A JP2005378304 A JP 2005378304A JP 2005378304 A JP2005378304 A JP 2005378304A JP 5085866 B2 JP5085866 B2 JP 5085866B2
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Description
本発明は、例えば河川・湖沼に堆積した、水を含む土壌を脱水減量化するのに好適に使用可能な袋体、および水を含む土壌を脱水減量化して、土壌を袋体の内部に封じ込めることが可能な含水土壌の脱水用袋体に関するものである。 INDUSTRIAL APPLICABILITY The present invention, for example, a bag body that can be suitably used for dehydrating and reducing water-containing soil deposited in rivers and lakes, and dehydrating and reducing water-containing soil to contain the soil inside the bag body. The present invention relates to a bag for dehydration of water-containing soil.
従来より、織物や不織布製の袋に、水、及びダイオキシンやPCBなどの有害物質を含む汚染土壌を充填し、脱水減量化して汚染土壌封じ込める工法が提案されており、例えば、特開2002−178000号公報には化学繊維製の透水性袋体を使用し、汚染土壌を圧入して加圧脱水したり、該袋体を順次積み重ねて下側の袋体を加圧脱水する方法が開示されている。 Conventionally, a construction method has been proposed in which contaminated soil containing toxic substances such as water and dioxin and PCB is filled in a woven fabric or non-woven fabric bag, dehydrated and reduced to contain the contaminated soil. No. 1 discloses a method of using a water-permeable bag made of chemical fiber and pressurizing and dehydrating by press-fitting contaminated soil, or stacking the bags sequentially and depressurizing the lower bag. Yes.
このような工法では、高含水土壌を、筒状の注入口から圧送ポンプに連なる注入ホースの先端部を挿入し注入する方法が多く用いられている。しかし注入した土壌がホースを抜いた際に逆流してこないようにするため、特許第3330026号公報には筒状注入口を袋体内部へ突出するように設置する方法が開示されている。 In such a construction method, a method of injecting highly water-containing soil by inserting the tip end portion of an injection hose connected to a pressure pump from a cylindrical injection port is often used. However, in order to prevent the injected soil from flowing back when the hose is pulled out, Japanese Patent No. 3330026 discloses a method of installing a cylindrical inlet so as to protrude into the bag body.
しかしながら、上記方法においては、土壌を注入した際、内部へ突出させた注入口が暴れてしまうため、注入速度を抑えなければならず、それを回避するためにホースを袋体内部へ突出した注入口より先まで挿入せねばならないが、その場合、注入終了後にホースを抜くと袋体内部筒状注入口をホースとともに引っ張り出すような状況が起こり、しばしば逆流防止の機能が果たせないという問題点を有していた。 However, in the above method, when the soil is injected, the injection port that protrudes to the inside is exposed, so that the injection speed must be suppressed. To avoid this, the hose is protruded into the bag body. In this case, if the hose is pulled out after the end of the injection, a situation may occur in which the inner cylindrical inlet of the bag is pulled out together with the hose, and the function of preventing backflow often cannot be performed. Had.
また袋体として、特開2002−178000号公報にはポリエステルやポリプロピレン等の化学繊維からなる袋体またその形態も不織布、織物、編物などが提示されている。しかしながら不織布では均一な目付けや厚さのものを得ることは難しく、高圧で注入すると低目付けや厚さの薄い部位に圧がかかり目が拡大してろ過効率が低下するという問題があり、また編物でも縫い目が拡大してろ過効率が低下するという問題があり、織物でも目詰まりや縫い目が裂けやすいという問題点があった。 Moreover, as a bag body, Japanese Patent Application Laid-Open No. 2002-178000 discloses a bag body made of chemical fibers such as polyester and polypropylene, and a non-woven fabric, a woven fabric, a knitted fabric and the like. However, it is difficult to obtain a fabric with a uniform basis weight and thickness with a non-woven fabric, and when injected at a high pressure, there is a problem that the pressure is applied to a low basis weight or a thin part and the eyes are enlarged to reduce the filtration efficiency. However, there is a problem that the filtration efficiency is lowered due to the expansion of the seam, and there is a problem that the seam is easily clogged and the seam is easily torn.
本発明の目的は、上記従来技術の有する問題点を解消し、河川・湖沼などに堆積する高含水量の土壌を効率良く、かつ、排水処理が不要なレベルまでろ過することが可能で、のり面などにおける含水土壌の封じ込め用袋体において、高含水土壌を注入する際、安定にかつ効率的に注入することができ、注入後の土壌逆流を防止できる袋体を提供することにある。 The object of the present invention is to solve the above-mentioned problems of the prior art, and to filter the high water content soil deposited in rivers, lakes, etc. efficiently and to a level that does not require wastewater treatment. It is an object of the present invention to provide a bag body that can stably and efficiently inject a highly water-containing soil in a bag body for containing water-containing soil on a surface or the like, and can prevent backflow of soil after the injection.
本発明者らは、上記目的を達成するため鋭意検討した結果、高含水比粘土を袋体に注入し袋詰め脱水する布帛製の袋詰脱水袋において、袋体への注入部を、袋体に取り付けた筒状体から構成し、該筒状体の内部への突出長が30cm以上500cm以下となり、かつ筒状体の端部径が注入口の径の1.5倍以上となるように袋体の内外部に突出するように形成した構造とすることにより解決できること、さらに袋体として特定のカバーファクターの織物を使用することにより安定にかつ効率よくろ過できることを見出した。 As a result of intensive studies to achieve the above-mentioned object, the present inventors have found that in a bag-filled dewatered bag made of a high moisture content clay poured into a bag body and dehydrated, the injection portion into the bag body is formed as a bag body. So that the projecting length to the inside of the cylindrical body is not less than 30 cm and not more than 500 cm, and the end diameter of the cylindrical body is not less than 1.5 times the diameter of the injection port It has been found that it can be solved by adopting a structure formed so as to protrude inside and outside of the bag body, and that it can be filtered stably and efficiently by using a fabric of a specific cover factor as the bag body.
本発明によれば、河川・湖沼などに堆積する高含水量の土壌を安定して効率良く、かつ、排水処理が不要なレベルまでろ過することが可能な袋体、およびこの袋体を用いた含水土壊の封じ込め方法が提供される。 According to the present invention, a bag body that can stably and efficiently filter soil having a high water content accumulated in rivers, lakes, and the like and to a level that does not require wastewater treatment, and the bag body are used. A method for containment of hydrous soil is provided.
本発明において、袋体への注入部は該袋体の内外部に突出するように形成された筒状体であり、該筒状体は、袋体内部への突出長が30cm以上500cm以下であることが必要である。30cmよりも短いと、十分な逆流防止効果がなく、ホースを抜いた際に注入した土壊が漏れ出る可能性がある。また、500cmよりも長い場合は、ホースを袋体奥まで挿入する必要があり、注入効率が悪い。 In this invention, the injection | pouring part to a bag body is a cylindrical body formed so that it might protrude inside and outside of this bag body, and this cylindrical body is 30 cm or more and 500 cm or less of protrusion length to the inside of a bag body. It is necessary to be. If it is shorter than 30 cm, there is no sufficient backflow prevention effect, and there is a possibility that the soil that has been injected when the hose is pulled out will leak. Moreover, when longer than 500 cm, it is necessary to insert a hose to the back of a bag body, and injection | pouring efficiency is bad.
一方、筒状体の径については、筒状体外部へ突出した端部に設けられた注入口の径に対し、内部に突出した最も奥部の排出口の径が1.5倍以上あり、内部へいくほど広がっていることが必要である。
径の比が1.5よりも小さい場合はホースより注入する際、ホース出口から注入口先までの間に高含水比土壌が通過すると、筒状注入口が暴れ、効率よく注入を行うことができない。
On the other hand, for the diameter of the cylindrical body, the diameter of the innermost outlet that protrudes to the inside is 1.5 times or more than the diameter of the inlet provided at the end protruding to the outside of the cylindrical body, It needs to spread as it goes inside.
When the ratio of diameters is smaller than 1.5, when the high water content soil passes between the hose outlet and the tip of the inlet when injecting from the hose, the cylindrical inlet is exposed and the injection cannot be performed efficiently. .
本発明で使用する合成繊維のマルチフィラメント糸としては、ポリエステル、ナイロン、ビニロン、ポリプロピレンなどのマルチフィラメント糸が例示され、中でもポリエステルマルチフィラメント糸であることが好ましい。特に、ポリエステルマルチフィラメント糸の中でも、良好な物性を示すポリエチレンテレフタレートマルチフィラメント糸や、袋体を恒久的に埋設しようとする場合は、生分解性の観点から、ポリ乳酸繊維からなるマルチフィラメント糸が好ましい。 Examples of the multifilament yarn of synthetic fiber used in the present invention include multifilament yarns such as polyester, nylon, vinylon, and polypropylene, and among them, polyester multifilament yarn is preferable. In particular, among polyester multifilament yarns, when a polyethylene terephthalate multifilament yarn showing good physical properties or a bag body is to be permanently embedded, a multifilament yarn made of polylactic acid fiber is used from the viewpoint of biodegradability. preferable.
また、上記のポリエステルマルチフィラメント糸は、再生ポリエステルからなるマルチフィラメント糸であることが好ましい。ここで、再生ポリエステルとは、回収ペットボトル、回収ボリエステル繊維、或いは回収ポリエステルフィルムなどから再生されたポリエステルを言い、回収したポリエステルを溶融して再度糸条に形成させるマテリアルリサイクル法や、回収したポリエステルを解重合して再度ボリマー化するケミカルリサイクル法により得られた再生ポリエステルなどが例示される。 The polyester multifilament yarn is preferably a multifilament yarn made of recycled polyester. Here, recycled polyester refers to polyester recycled from recovered PET bottles, recovered polyester fibers, recovered polyester film, etc., and the material recycling method in which the recovered polyester is melted to form yarn again, or recovered polyester Examples thereof include regenerated polyester obtained by a chemical recycling method in which a polymer is depolymerized and converted into a polymer again.
マテリアルリサイクル法の具体例としては、特開2000−29362号公報に開示される如く、回収されたポリエステルポリマーを、ビスオキサゾリン系化合物と溶融反応させて、該ポリエステルポリマーの固有粘度をO.5〜1.1とする方法、また、ケミカルリサイクル法の具体例としては、特開2003−160656号公報に開示される如く、回収されたポリアルキレンテレフタレートポリマーをメタノール解重合して得られたテレフタル酸ジメチルを70重量%以上使用し、かつ、触媒として、チタン化合物とリン化合物とを、チタン元素のモル数に対するリン元素のモル数(P/Ti)が特定の範囲となるように、グリコール中で加熱することにより得られた析出物を用いて重縮合反応させる方法などが例示される。 As a specific example of the material recycling method, as disclosed in JP-A-2000-29362, the recovered polyester polymer is melt-reacted with a bisoxazoline-based compound, and the intrinsic viscosity of the polyester polymer is changed to O.D. Specific examples of the method of 5 to 1.1 and the chemical recycling method include terephthalates obtained by methanol depolymerization of recovered polyalkylene terephthalate polymers, as disclosed in JP-A-2003-160656. Dimethyl acid is used in an amount of 70% by weight or more as a catalyst, and a titanium compound and a phosphorus compound are used in a glycol so that the number of moles of phosphorus element (P / Ti) relative to the number of moles of titanium element falls within a specific range. Examples thereof include a method of polycondensation reaction using a precipitate obtained by heating at a temperature.
なお、上記マルチフィラメント糸の総繊度は、通常、75〜2000dtex、好ましくは150〜1500dtexであり、また、総フィラメント数は、通常、75〜2000フィラメント、好ましくは150〜1500フィラメントである。上記の合成繊維のマルチフィラメント糸は、常法により織成されて織物とされ、該織物を用いて袋体が形成される。 The total fineness of the multifilament yarn is usually 75 to 2000 dtex, preferably 150 to 1500 dtex, and the total number of filaments is usually 75 to 2000 filaments, preferably 150 to 1500 filaments. The synthetic filament multifilament yarn is woven into a woven fabric by a conventional method, and a bag is formed using the woven fabric.
ここで、袋体に使用する織物のカバーファクター(CF)が、1900〜2700であることが必要である。好ましくは2100〜2500である。カバーファクター(CF)は下記の式で算出した。
CF=(DWp/1.1)1/2×MWp+(DWf/1.1)1/2×MWf
ここで、DWpは経糸総繊度(dtex)、MWpは経糸織密度(本/3.79cm)、DWfは緯糸総繊度(dtex)、MWfは緯糸織密度(本/3.79cm)である。また織組織、層数は特に限定されるものではない。例えば、織組織としては平組織、綾組織、サテンなどが好適に例示されるがこれらに限定されるものではない。また、層数も単層でもよいし2層以上の多層であってもよい。
Here, the cover factor (CF) of the woven fabric used for the bag body needs to be 1900-2700. Preferably it is 2100-2500. The cover factor (CF) was calculated by the following formula.
CF = (DWp / 1.1) 1/2 × MWp + (DWf / 1.1) 1/2 × MWf
Here, DWp is the total warp fineness (dtex), MWp is the warp weave density (main / 3.79 cm), DWf is the total weft fineness (dtex), and MWf is the weft weave density (main / 3.79 cm). The woven structure and the number of layers are not particularly limited. For example, preferred examples of the woven structure include a plain structure, a twill structure, and satin, but are not limited thereto. The number of layers may be a single layer or a multilayer of two or more layers.
上記カバーファクター(CF)は、式から明らかなように織物を構成する経糸,緯糸の繊度や密度により、適宜調整することができる。このカバーファクターが1900より低い場合は、高圧で土壌を注入する際、メッシュの開口径が大きくなり、ろ過性が低下したり、また袋体の縫い目が拡大し、ろ過されない土壌や有害物質が流出する問題がある。またカバーファクターが2700より高い場合はメッシュ目が目詰まりし、ろ過速度が低下する。 The cover factor (CF) can be appropriately adjusted according to the fineness and density of the warp and weft constituting the woven fabric as is apparent from the equation. When this cover factor is lower than 1900, when injecting soil at high pressure, the mesh opening diameter increases, filterability decreases, and the seam of the bag expands, causing unfiltered soil and harmful substances to flow out. There is a problem to do. On the other hand, when the cover factor is higher than 2700, the mesh is clogged and the filtration rate is lowered.
かくして、本発明によれば、高含水比粘土を袋体に注入し袋詰脱水する布串製の袋詰脱水袋において、袋体への注入部を、袋体に取り付けた筒状体から構成し、該筒状体の内部への突出長が30cm以上500cm以下となり、かつ筒状体の端部径が注入口の径の1.5倍以上となるように袋体の内外部に突出するように形成された構造とすること、含水土壌の脱水用袋体が合成繊維のマルチフィラメント糸織物からなる袋体において、該合成繊維のマルチフィラメント糸織物のカバーファクターが1900〜2700とすることにより、有害物質を含む汚染土壌を、上記袋体内に入れた後、該袋体内の汚染土壌に含まれる水分を袋体外に安定に透過させて脱水することが出来るとともに、汚染土壌に付着した有害物質を袋体内に封じ込めることができる。 Thus, according to the present invention, in the bag dewatering bag made of cloth skewer for injecting high water content clay into the bag body and bagging and dewatering, the injection portion to the bag body is composed of a cylindrical body attached to the bag body And projecting into and out of the bag body so that the projecting length to the inside of the cylindrical body is 30 cm or more and 500 cm or less, and the end diameter of the cylindrical body is 1.5 times or more the diameter of the injection port. And the cover factor of the multifilament yarn fabric of synthetic fibers is 1900-2700 when the bag for dehydration of the hydrous soil is made of a synthetic filament multifilament yarn fabric. In addition, after putting contaminated soil containing harmful substances into the bag, moisture contained in the contaminated soil in the bag can be stably permeated to the outside of the bag to dehydrate, and harmful substances attached to the contaminated soil. In the bag Door can be.
以下、実施例により本発明をさらに具体的に説明する。 Hereinafter, the present invention will be described more specifically with reference to examples.
[実施例1−9、比較例1−3]
土壌の作成:霞ヶ浦粘土を含水比300%の泥水状に調整した。
袋体の作成:ポリエステル製の平織物を縫製し、周長8m、長さ20mの袋材を作製した。
[Example 1-9, Comparative Example 1-3]
Soil preparation: Kasumigaura clay was adjusted to a muddy water state with a water content of 300%.
Production of bag: A plain fabric made of polyester was sewn to produce a bag material having a circumference of 8 m and a length of 20 m.
表1、実施例1〜7に示すようなサイズの注入口を設け、ポンプにより上記作成の土壌を注入し、その状況を観察した。その際、ホースは注入口筒状体全長の2分の1のところまで挿入した。これらの構造をとることにより安定して含水土壌を注入でき、ろ過も良好であった。比較例1〜3では逆流したり、筒状体があばれたり、詰まりが生じるなど問題であった。 実施例8、9ではカバーファクター2000と2600のものを使用したが非常にろ過効率が良く、逆に比較例4ではカバーファクターが1500と低いため、ろ過漏れを起こし、比較例5では3000と高いため、逆に目詰まりを起こし効率が悪くなり問題であった。 The inlet of the size as shown in Table 1 and Examples 1 to 7 was provided, and the above-prepared soil was injected with a pump, and the situation was observed. At that time, the hose was inserted up to a half of the entire length of the inlet cylindrical body. By taking these structures, the water-containing soil could be injected stably and the filtration was also good. In Comparative Examples 1 to 3, there were problems such as backward flow, tubular bodies being broken, and clogging. In Examples 8 and 9, those with cover factors 2000 and 2600 were used, but the filtration efficiency was very good. Conversely, since Comparative Example 4 had a low cover factor of 1500, filtration leakage occurred, and Comparative Example 5 had a high value of 3000. Therefore, clogging occurs on the contrary and the efficiency is deteriorated, which is a problem.
本発明によれば、有害物質を含む含水土壊の封じ込めに好適に使用可能な袋体、およびこの袋体を用いた含水土壊の封じ込め方法が提供されるので、ダイオキシン類、PCB、砒素、鉛等の河川・湖沼などに堆積する有害物質を含む高含水土壌を効率良く、かつ、排水処理が不要なレベルまでろ過することができる。 According to the present invention, there is provided a bag body that can be suitably used for containment of hydrous soil containing harmful substances, and a method for containing hydrous soil breakage using this bag body, so that dioxins, PCBs, arsenic, Highly water-containing soil containing harmful substances deposited in rivers and lakes such as lead can be filtered efficiently to a level that does not require wastewater treatment.
Claims (10)
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| Application Number | Priority Date | Filing Date | Title |
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| JP2005378304A JP5085866B2 (en) | 2005-12-28 | 2005-12-28 | Bag for dehydration of hydrous soil |
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| JP2005378304A JP5085866B2 (en) | 2005-12-28 | 2005-12-28 | Bag for dehydration of hydrous soil |
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| JP2007175642A JP2007175642A (en) | 2007-07-12 |
| JP5085866B2 true JP5085866B2 (en) | 2012-11-28 |
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| JP4754977B2 (en) * | 2006-02-03 | 2011-08-24 | 株式会社ピーエス三菱 | Bagging dehydration method and equipment |
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| JPS5332810Y2 (en) * | 1973-04-04 | 1978-08-14 | ||
| JP3330026B2 (en) * | 1996-07-29 | 2002-09-30 | 独立行政法人土木研究所 | Filler structure of bag dewatering bag |
| JP3376304B2 (en) * | 1998-12-16 | 2003-02-10 | 前田工繊株式会社 | Civil engineering bag with leakage prevention function |
| JP2001123427A (en) * | 1999-10-25 | 2001-05-08 | Unitika Ltd | Bag body for civil engineering |
| JP3493413B2 (en) * | 2000-12-14 | 2004-02-03 | 独立行政法人土木研究所 | Methods for containment of hazardous substances |
| JP3807619B2 (en) * | 2003-06-24 | 2006-08-09 | 帝人テクノプロダクツ株式会社 | Contained soil containment method and contaminated soil containment bag |
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