JP2005279324A - Method for improving mud quality and water quality of tide-sensitive river - Google Patents

Method for improving mud quality and water quality of tide-sensitive river Download PDF

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JP2005279324A
JP2005279324A JP2004093124A JP2004093124A JP2005279324A JP 2005279324 A JP2005279324 A JP 2005279324A JP 2004093124 A JP2004093124 A JP 2004093124A JP 2004093124 A JP2004093124 A JP 2004093124A JP 2005279324 A JP2005279324 A JP 2005279324A
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water quality
mud
river
water
improving
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JP3912682B2 (en
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Mitsuhiko Suekuni
光彦 末國
Toshinori Oda
敏範 尾田
Katsumi Iwai
克己 岩井
Tadashi Hibino
忠史 日比野
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NIPPON MIKUNIYA KK
Chugoku Electric Power Co Inc
Chuden Engineering Consultants Co Ltd
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NIPPON MIKUNIYA KK
Chugoku Electric Power Co Inc
Chuden Engineering Consultants Co Ltd
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
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    • Y02W10/10Biological treatment of water, waste water, or sewage

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Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for improving the mud quality and water quality of tide-sensitive rivers capable of improving the mud quality and water quality of the tide-sensitive rivers by supplying oxygen to bottom mud using the tiding of the tide-sensitive rivers. <P>SOLUTION: A mud quality/water quality improving cylinder 10 is filled with a modified material 21 good in water permeability and embedded in the river beds of the tide-sensitive rivers 1. Herein, the modified material 21 may be embedded in the river beds so that the upper surfaces of the mud quality/water quality improving cylinders 10 become to vicinity of the surfaces of mud deposited on the river beds of the tide-sensitive rivers 1. Further, the modified material 21 may be solid particulates such as stones, alkaline solid particulates or coal ash solid particulates. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、感潮河川の潮汐を利用して感潮河川に堆積した底泥の性状(以下、「泥質」という。)および河川水の水質を合理的な方法により浄化して河川環境の改善を図ることができる感潮河川の泥質および水質改善方法に関するものである。   The present invention uses a tide of a tidal river to purify the nature of the bottom mud accumulated in the tidal river (hereinafter referred to as “mud”) and the water quality of the river water by a rational method. It relates to a method for improving mud quality and water quality of tidal rivers that can be improved.

たとえば広島市の太田川のような都市型河川(特に、潮の干満がある感潮河川)は、「流水の停滞」、「ヘドロの堆積」、「栄養塩の河川流入の増大」などにより河川浄化機能が損なわれつつあり、これにより以下に示すような状況を惹起している。
(1)水質の悪化、悪臭(硫化水素など)の発生
(2)水辺景観価値の喪失および人々の水辺離れ
(3)人の流動性の低下および都市活性化の阻害
このような状況の下、河川管理者らは都市型河川(特に、感潮河川)の浄化への取り組みを推進している。
For example, urban rivers such as the Ota River in Hiroshima City (especially tidal rivers with tides) are rivers due to “stagnation of running water”, “deposition of sludge”, “increasing nutrient inflow of nutrients”, etc. The purification function is being impaired, and this causes the following situation.
(1) Deterioration of water quality, generation of bad odors (hydrogen sulfide, etc.) (2) Loss of waterside landscape value and separation of people from watersides (3) Decline in human mobility and inhibition of urban activation Under these circumstances, River managers are promoting efforts to purify urban rivers (especially tidal rivers).

従来、河川の水質を浄化する方法としては、たとえば以下に示す3つの特許文献に開示されているものがある。
特開平5−131196号公報 特開平10−15538号公報 特開2001−29951号公報
Conventionally, as a method for purifying the water quality of a river, for example, there are those disclosed in the following three patent documents.
JP-A-5-131196 Japanese Patent Laid-Open No. 10-15538 JP 2001-29951 A

上記特許文献1(特開平5−131196号公報)は、自然の汚染された水質環境は一般に酸性状態になっていることが多いことから、アルカリ性を有する貝殻およびアルカリ性固体粒体(鉱滓、石炭灰、セメントレータンスなど)を透水性の枠体内に充填した環境浄化構造体を水中に設置することにより、貝殻やアルカリ性固体粒体中のアルカリ分を水中に溶け出させて、酸性状態にある汚染水を中和したり緩和したりして、海、港湾、河川、沼湖、池、ダムなどの水質環境を浄化することを開示する。
また、上記特許文献1は、水浄化作用を有する有用微生物や小動物が貝殻およびアルカリ性固体粒体の表面に棲息・増殖してその水浄化作用を一層促進することができることも開示している。
Patent Document 1 (Japanese Patent Application Laid-Open No. 5-131196) discloses that a natural polluted water environment is generally in an acidic state. Therefore, shells and alkaline solid particles having an alkalinity (slag, coal ash) Contamination, etc.) In the water, an environmental purification structure filled with a water-permeable frame is used to dissolve the alkali in the shells and alkaline solid particles into the water, resulting in acid pollution. Disclose the purification of water environments such as seas, harbors, rivers, marshes, ponds, dams, etc. by neutralizing or mitigating water.
Moreover, the said patent document 1 is also disclosing that the useful microbe and small animal which have a water purification effect can inhabit and propagate on the surface of a shell and an alkaline solid granule, and can further promote the water purification effect.

上記特許文献2(特開平10−15538号公報)は、アンモニア態窒素、亜硝酸態窒素、リン酸態リンの吸収剤とした熱処理貝化石を水底に投入することにより、底質やその近辺の海域のマイナス要因たる物資を速やかに減衰させることにより、底質および水質の改善を図るとともに、底棲動物にとって良好な環境を現出させることを開示している。   Patent Document 2 (Japanese Patent Application Laid-Open No. 10-15538) discloses that a heat-treated shell fossil used as an absorbent of ammonia nitrogen, nitrite nitrogen, and phosphorous phosphorus is introduced into the bottom of the water, so that the bottom sediment and the vicinity thereof can be obtained. It is disclosed that by promptly attenuating materials that are negative factors in the sea area, the bottom quality and water quality are improved, and a good environment for benthic animals appears.

上記特許文献3(特開2001−29951号公報)は、石炭灰に水熱化学処理を施して得られる人工ゼオライトを海域の底質泥土層の上部面に敷設することにより、内湾などといった閉鎖的な海域における栄養塩やガスによる富栄養化などにより生じる水質汚濁を防止することを開示している。   Patent Document 3 (Japanese Patent Application Laid-Open No. 2001-29951) discloses that an artificial zeolite obtained by subjecting coal ash to hydrothermal chemical treatment is laid on the upper surface of a sedimentary mud layer in a sea area, thereby closing the inner bay. Is disclosed to prevent water pollution caused by eutrophication with nutrient salts and gas in various sea areas.

しかしながら、上記3つの特許文献はいずれも改質材料(泥質・水質改善剤)を水中(海中)に沈めて常に水(海水)に晒すものであり、底泥への酸素供給により還元状態を解消することによって河川の底質や水質を改善する方法については何ら開示されていない。   However, the above three patent documents all saturate the reforming material (mud quality / water quality improving agent) in the water (in the sea) and always expose it to the water (sea water). There is no disclosure about how to improve river bottom quality and water quality by eliminating it.

本発明の目的は、感潮河川の潮汐を利用した底泥への酸素供給による河川の底質の改善および底泥の浄化作用を誘起する底棲生物の良好な生息環境の現出による底質の改善促進するだけでなく、河川の水質の改善も図ることができる泥質および水質改善方法を提供することにある。   The object of the present invention is to improve the bottom quality of the river by oxygen supply to the bottom mud using the tide of the tidal river and to reveal the good habitat environment of the bottom organism that induces the purification action of the bottom mud. It is to provide a method for improving mud quality and water quality that can not only promote improvement of water quality but also improve water quality of rivers.

本発明の潮の干満がある感潮河川(1)の泥質および水質改善方法は、透水性のよい改質材料(21)を該改質材料(21)と底泥の間の流動を阻害しない容器である泥質・水質改善筒(10)に充填し、該泥質・水質改善筒(10)を前記感潮河川(1)の河床に埋設することを特徴とする。
前記泥質・水質改善筒(10)を該泥質・水質改善筒(10)の上面が前記感潮河川(1)の河床に溜まった泥土の表面付近となるように該河床に埋設してもよい。
前記改質材料(21)が、礫などの固形粒体であってもよい。
前記改質材料(21)が、アルカリ性固形粒体であってもよい。
前記改質材料(21)が、火力発電所から発生する石炭灰を主材料に加水混合して造粒方法により粒状にした石炭灰材料(以下、「石炭灰造粒物」という。)であってもよい。
前記改質材料(21)がアルカリ性固形粒体あるいは石炭灰造粒物の場合、アルカリ性固形粒体あるいは石炭灰造粒物がもつ水中に溶存したリンの不溶化・固定化(以下「リンの固定化」という。)の能力が飽和状態となった前記改質材料(21)を回収し、該回収した前記改質材料(21)をたとえば透水性土木材料として活用してもよい。
The method for improving the mud quality and water quality of a tidal river (1) with tides according to the present invention inhibits the flow between the modified material (21) and the bottom mud with the modified material (21) having good water permeability. The muddy / water quality improvement cylinder (10) which is a non-contained container is filled, and the muddy / water quality improvement cylinder (10) is embedded in the river bed of the tidal river (1).
The muddy / water quality improvement cylinder (10) is embedded in the river bed so that the upper surface of the muddy / water quality improvement cylinder (10) is close to the surface of the mud collected in the river bed of the tidal river (1). Also good.
The modified material (21) may be a solid particle such as gravel.
The modifying material (21) may be an alkaline solid particle.
The modified material (21) is a coal ash material (hereinafter referred to as “coal ash granulated material”) obtained by adding coal ash generated from a thermal power plant to a main material and granulating it with a granulation method. May be.
When the modified material (21) is an alkaline solid granule or coal ash granule, the insoluble / immobilized phosphorus dissolved in water of the alkaline solid granule or coal ash granule (hereinafter referred to as "immobilization of phosphorus"). The modified material (21) whose ability has been saturated may be recovered, and the recovered modified material (21) may be utilized as, for example, a water-permeable civil engineering material.

本発明の潮の干満がある感潮河川の泥質および水質改善方法は、以下に示すような効果を奏する。
(1)透水性のよい改質材料を充填した泥質・水質改善筒を感潮河川の河床に埋設することで、感潮河川の潮汐により底泥に酸素が供給され、底泥の還元状態が解消する。また、泥質・水質改善筒を底泥下部の砂礫層まで到達させることで、より多くの酸素が供給される。これにより、硫化水素の発生が抑制されるとともに、底泥が好気性状態となることで底泥中の窒素などが除去できる。また、底泥および泥質・水質改善筒内およびその周囲に底泥の浄化作用を誘起する生物の良好な生息環境を現出することができ、一層泥質の改善が促進される。
(2)アルカリ性固形粒体や石炭灰造粒物は、底泥中のリンの固定化能力を有することから底質の改善が図られるばかりでなく、底泥中に含まれるリンの固定化により水中へのリンの溶出が抑制でき、河川の水質の改善を図ることができる。
(3)石炭灰造粒物を改質材料として使用することにより、火力発電所から発生する石炭灰の有効活用を図ることができる。
(4)リンの固定化能力が飽和状態となった改質材料を回収し、回収した改質材料をたとえば透水性土木材料として活用することができる。
The mud and water quality improvement method for a tidal river with tides according to the present invention has the following effects.
(1) By burying a muddy / water quality improvement cylinder filled with a material with good permeability in the river bed of the tidal river, oxygen is supplied to the bottom mud by the tide of the tidal river, and the bottom mud is reduced. Disappears. Moreover, more oxygen is supplied by reaching the muddy / water quality improvement cylinder to the gravel layer below the bottom mud. Thereby, generation | occurrence | production of hydrogen sulfide is suppressed, and nitrogen etc. in bottom mud can be removed because bottom mud will be in an aerobic state. In addition, a good habitat for living organisms that induce the purification action of the bottom mud can be produced in and around the bottom mud and the mud / water quality improvement cylinder, and the improvement of the mud quality is further promoted.
(2) Alkaline solid granules and coal ash granulates have the ability to fix phosphorus in the bottom mud, so that not only the bottom quality is improved, but also the phosphorus contained in the bottom mud is fixed. Elution of phosphorus into water can be suppressed, and river water quality can be improved.
(3) By using coal ash granulated material as a reforming material, it is possible to effectively utilize coal ash generated from a thermal power plant.
(4) The modified material in which the phosphorus immobilization ability is saturated can be recovered, and the recovered modified material can be used as, for example, a permeable civil engineering material.

感潮河川の潮汐を利用した底泥への酸素供給による河川の泥質および水質の改善という目的を、感潮河川の潮汐を利用して透水性のよい改質材料およびそれに接する底泥内に水の流れを生じさせて酸素を供給し、好気性環境を現出させることにより実現した。
また、赤潮などの誘因物質であるリンの固定化による河川の泥質および水質の改善という目的を、アルカリ性固形粒体あるいは石炭灰造粒物を用いることで実現した。
The purpose of improving river mud quality and water quality by supplying oxygen to the bottom mud using the tide of the tidal river is to improve the permeability of the tidal river and the bottom mud in contact with it. This was realized by creating aerobic environment by supplying oxygen by generating water flow.
In addition, the purpose of improving the mud and water quality of rivers by fixing phosphorus, which is an inducer such as red tide, was realized by using alkaline solid particles or coal ash granules.

以下、本発明の感潮河川の泥質および水質改善方法の実施例について図面を参照して説明する。
図1は、本発明の実施例による感潮河川の泥質および水質改善方法を説明するための泥質・水質改善筒設置横断面図であり、図2は、本発明の実施例による感潮河川の泥質および水質改善方法を説明するための泥質・水質改善筒設置平面図である。
本実施例による感潮河川の泥質および水質改善方法では、図1に示すように、透水性のよい改質材料21が充填された泥質・水質改善筒10は、潮の干満がある感潮河川1の河床に多数個埋設される。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Embodiments of the method for improving the quality and quality of tidal rivers according to the present invention will be described below with reference to the drawings.
FIG. 1 is a horizontal cross-sectional view of a muddy / water quality improvement cylinder for explaining a method for improving muddy and water quality of a tidal river according to an embodiment of the present invention, and FIG. 2 is a tidal sense according to an embodiment of the present invention. It is a muddy / water quality improvement cylinder installation top view for demonstrating the muddy nature of a river, and a water quality improvement method.
In the tidal river water quality improvement method according to the present embodiment, as shown in FIG. 1, the muddy / water quality improvement cylinder 10 filled with the highly water-permeable modifying material 21 has a feeling of tides. Many are buried in the riverbed of the tidal river 1.

また、各泥質・水質改善筒10は、その上面が河床に溜まった泥土(たとえば、ヘドロ層)の表面付近となるように埋設される。これによって、潮汐により溶存酸素を含んだ河川水が泥質・水質改善筒10内を効果的に通過することができるとともに、干潮時には各泥質・水質改善筒10を介して底泥に酸素を供給することができる。   Further, each of the muddy / water quality improvement cylinders 10 is embedded so that the upper surface thereof is in the vicinity of the surface of muddy soil (for example, sludge layer) accumulated on the river bed. As a result, river water containing dissolved oxygen due to the tide can effectively pass through the muddy / water quality improvement cylinder 10 and oxygen can be added to the bottom mud through each muddy / water quality improvement cylinder 10 at low tide. Can be supplied.

さらに、各泥質・水質改善筒10は、図2に示すように、円筒形をしており、河川の岸に沿って間隔Lの千鳥となるように配置することにより効果的な改質範囲Cを得ることができる。   Further, as shown in FIG. 2, each of the muddy / water quality improvement cylinders 10 has a cylindrical shape, and an effective reforming range is provided by arranging the muddy / water quality improvement cylinders 10 in a staggered manner along the river shore. C can be obtained.

泥質・水質改善筒10に充填される改質材料21としては、上記特許文献1(特開平5−131196号公報)に開示されているような石炭灰、赤土、炭酸カルシウムなどのアルカリ性物質を少量のセメントなどの結合剤で固めて粒体化したものを用いることができるが、以下に示すような石炭灰造粒物を用いることにより、石炭灰の有効活用が図れる。   As the reforming material 21 filled in the muddy / water quality improvement cylinder 10, alkaline substances such as coal ash, red clay, calcium carbonate as disclosed in the above-mentioned Patent Document 1 (Japanese Patent Laid-Open No. 5-131196) are used. Although it is possible to use a material that has been solidified with a small amount of a binder such as cement, it is possible to effectively use coal ash by using a coal ash granule as shown below.

石炭灰造粒物は、たとえば石炭焚流動床式火力発電所の燃焼灰(以下、「流動床灰」と称する。)100%と水15%(流動床灰に対して)を混合することにより直径10〜15mmの大きさの粒にする造粒方法により製造され、表1に一例を示すような物理特性を有する。
Coal ash granulated material is obtained by, for example, mixing 100% combustion ash (hereinafter referred to as “fluidized bed ash”) of coal-fired fluidized bed thermal power plant and 15% water (relative to fluidized bed ash). Manufactured by a granulation method to make particles having a diameter of 10 to 15 mm, and has physical properties as shown in Table 1.

また、石炭灰造粒物は、図3に試験結果の一例(流動床灰を用いた石炭灰造粒物による底泥中のリン除去性能)を示すように、リン除去性能が優れており、富栄養化海域にこれまで採られてきた敷砂による被覆対策に比べて、石炭灰造粒物は、原材料である石炭灰のリンの固定化効果を最大限活かした材料であるため、天然砂に比べて赤潮などの原因となるリンの固定化により水中への溶出を防止する能力を有する。
また、流動床灰を用いた石炭灰造粒物は、「海洋の汚染に係る環境基準」の環境項目を全項目満足する安全な材料でもある。
さらに、流動床灰を用いた石炭灰造粒物は、取扱いが容易でありかつ長期に安定な形状が保持できる材料でもある。
In addition, the coal ash granule has excellent phosphorus removal performance as shown in FIG. 3 as an example of the test results (phosphorus removal performance in bottom mud by coal ash granulation using fluidized bed ash). Compared to the conventional measures to cover eutrophic seawater with coal sand, coal ash granulation is a material that maximizes the effect of fixing phosphorus in coal ash, which is a raw material. Compared with, it has the ability to prevent elution into water by immobilizing phosphorus which causes red tides.
In addition, coal ash granulated material using fluidized bed ash is also a safe material that satisfies all the environmental items of the “environmental standards related to marine pollution”.
Furthermore, the coal ash granule using fluidized bed ash is a material that is easy to handle and can maintain a stable shape for a long time.

以上説明したように、本実施例による感潮河川の泥質および水質改善方法では、以下に示すような泥質および水質の改善効果がある。
(1)泥質の改善効果
(a)潮汐により、各泥質・水質改善筒10内に溶存酸素を含んだ水の流れを生じさせることができるため、あるいは干潮時には各泥質・水質改善筒10を介して底泥に酸素が供給できるため、底泥の還元状態を解消することができる。
(b)底泥への酸素の供給により、硫化水素などの発生が抑制できるとともに、底泥のヘドロ化が防止できる。
(c)底棲生物の良好な生息環境が現出できることにより、相乗的に改質範囲が拡大できる。
(d)底泥への酸素の供給により、底泥が好気性状態となり窒素などが除去できる。また、アルカリ性固形粒体や石炭灰造粒物を用いることにより底泥中のリンの固定化が図られ、河川水へのリンの溶出が抑制できる。
(2)水質の改善効果
(a)底泥の還元状態の解消により窒素などが除去されることから河川水への溶出が抑制できる。
(b)改質材料21にアルカリ性固形粒体や石炭灰造粒物などを用いることにより、リンの固定化が図られることから河川水へのリンの溶出を抑制することができるとともに、水中のリンの固定化を図ることができる。
As described above, the method for improving the quality and quality of tidal rivers according to the present embodiment has the following effects of improving the quality and quality of water.
(1) Effect of improving mud quality (a) Since the flow of water containing dissolved oxygen can be generated in each mud / water quality improvement cylinder 10 by tide, or each mud / water quality improvement cylinder at low tide Since oxygen can be supplied to the bottom mud through 10, the reduced state of the bottom mud can be eliminated.
(B) By supplying oxygen to the bottom mud, generation of hydrogen sulfide and the like can be suppressed, and sludge formation of the bottom mud can be prevented.
(C) Since a good habitat environment for benthic organisms can appear, the range of modification can be expanded synergistically.
(D) By supplying oxygen to the bottom mud, the bottom mud becomes aerobic and nitrogen and the like can be removed. Moreover, by using alkaline solid particles or coal ash granulated material, phosphorus in the bottom mud can be immobilized, and elution of phosphorus into river water can be suppressed.
(2) Water quality improvement effect (a) Elution to river water can be suppressed because nitrogen and the like are removed by eliminating the reduced state of the bottom mud.
(B) By using alkaline solid particles or coal ash granulated material as the reforming material 21, phosphorus can be immobilized, so that elution of phosphorus into river water can be suppressed, Immobilization of phosphorus can be achieved.

また、アルカリ性固形粒体や石炭灰造粒物を用いる場合、リンの固定化の効果が飽和状態となった改質材料21を回収して新しい改質材料21に容易に交換することができるとともに、回収した改質材料21をたとえば透水性土木材料として活用することができる。   When alkaline solid particles or coal ash granules are used, the reforming material 21 in which the effect of fixing phosphorus is saturated can be recovered and easily replaced with a new reforming material 21. The recovered modified material 21 can be used as, for example, a water-permeable civil engineering material.

なお、以上の説明では、泥質・水質改善筒10を円筒形のものとしたが、その形状は任意の形状(たとえば、矩形筒)でよい。また、泥質・水質改善筒10を河床に配置する方法は、図2に示した方法に限られず、任意のパターンで配置してもよい。   In the above description, the muddy / water quality improvement cylinder 10 is cylindrical, but the shape may be any shape (for example, a rectangular cylinder). Moreover, the method of arrange | positioning the muddy / water quality improvement cylinder 10 in a river bed is not restricted to the method shown in FIG. 2, You may arrange | position with arbitrary patterns.

以上説明したように、本発明の感潮河川の泥質および水質改善方法によれば、都市型河川で問題となっているヘドロの堆積による水質の悪化や悪臭の発生、水辺景観価値の喪失および人々の水辺離れ、人の流動性の低下および都市活性化の阻害などを防止することができる。
また、石炭灰造粒物を改質材料として使用することにより、火力発電所から発生する石炭灰を有効活用することができる。
As described above, according to the mud and water quality improvement method of the tidal river of the present invention, the deterioration of water quality due to sludge accumulation and the generation of bad odor, the loss of waterside landscape value and It is possible to prevent people from leaving the water, people from falling in fluidity, and urban activation.
Moreover, the coal ash generated from the thermal power plant can be effectively utilized by using the coal ash granulated material as a reforming material.

本発明の第1の実施例による感潮河川の泥質および水質改善方法を説明するための泥質・水質改善筒設置横断面図である。(実施例1)It is a mud and water quality improvement cylinder installation cross-sectional view for demonstrating the mud quality and water quality improvement method of a tidal river by the 1st Example of this invention. (Example 1) 本発明の第1の実施例による感潮河川の泥質および水質改善方法を説明するための泥質・水質改善筒設置平面図である。(実施例1)It is a muddy / water quality improvement cylinder installation top view for demonstrating the muddy quality of a tidal river and the water quality improvement method by 1st Example of this invention. (Example 1) 改質材料として用いた流動床灰を用いた人工骨材のリン除去性能を測定した試験結果の一例を示す図である。(実施例1)It is a figure which shows an example of the test result which measured the phosphorus removal performance of the artificial aggregate using the fluidized bed ash used as a modifying material. (Example 1)

符号の説明Explanation of symbols

1 感潮河川
10 泥質・水質改善筒
21 改質材料
C 改質範囲
L 間隔
1 Tidal river 10 Mud and water quality improvement cylinder 21 Reforming material C Reforming range L Interval

Claims (6)

潮の干満がある感潮河川(1)の泥質および水質改善方法であって、
底泥および水中のリンを不溶化・固定化しかつ透水性のよい改質材料(21)を該改質材料(21)と底泥との間の水の流れを阻害しない容器である泥質・水質改善筒(10)に充填し、該泥質・水質改善筒(10)を前記感潮河川(1)の河床に埋設することを特徴とする、感潮河川の泥質および水質改善方法。
A method for improving the mud and water quality of a tidal river (1) with tides,
Mud and water quality which is a container in which the bottom mud and phosphorus in water are insolubilized and fixed and the water-permeable modified material (21) does not hinder the flow of water between the modified material (21) and the bottom mud. A method for improving the tide and water quality of a tidal river, wherein the improvement cylinder (10) is filled and the muddy / water quality improvement cylinder (10) is buried in the river bed of the tidal river (1).
前記泥質・水質改善筒(10)を該泥質・水質改善筒(10)の上面が前記感潮河川(1)の河床に溜まった泥土の表面付近となるように該河床に埋設することを特徴とする、請求項1記載の感潮河川の泥質および水質改善方法。   The muddy / water quality improvement cylinder (10) is embedded in the river bed so that the upper surface of the muddy / water quality improvement cylinder (10) is close to the surface of the mud collected in the river bed of the tidal river (1). The method for improving mud and water quality of a tidal river according to claim 1. 前記改質材料(21)が礫などの固形粒体であることを特徴とする、請求項1または2記載の感潮河川の泥質および水質改善方法。   The method for improving mud and water quality of tidal rivers according to claim 1 or 2, characterized in that the modifying material (21) is a solid granule such as gravel. 前記改質材料(21)がアルカリ性固形粒体であることを特徴とする、請求項1または2記載の感潮河川の泥質および水質改善方法。   The method for improving mud and water quality of tidal rivers according to claim 1 or 2, wherein the modifying material (21) is an alkaline solid particle. 前記改質材料(21)が、石炭灰を主材料に加水混合して造粒方法により粒状にした石炭灰材料であることを特徴とする、請求項4記載の感潮河川の泥質および水質改善方法。   The mud and water quality of a tidal river according to claim 4, characterized in that the modified material (21) is a coal ash material obtained by adding coal ash to a main material and granulating it by a granulation method. How to improve. 前記リンの不溶化・固定化の効果が飽和状態となった前記改質材料(21)を回収し、該回収した改質材料(21)を透水性土木材料として活用することを特徴とする、請求項1記載の感潮河川の泥質および水質改善方法。

The modified material (21) in which the effect of insolubilization / immobilization of phosphorus is saturated is recovered, and the recovered modified material (21) is utilized as a permeable civil engineering material. Item 1. A method for improving mud and water quality in a tidal river.

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JP2011173100A (en) * 2010-02-25 2011-09-08 Chugoku Electric Power Co Inc:The Granular material for water purification and water purification method
JP2012223733A (en) * 2011-04-21 2012-11-15 Hiroshima Univ Method for improving ambient water quality
CN106242214A (en) * 2016-08-22 2016-12-21 苏州科技大学 A kind of method strengthening enclosed type Sediments Endogenous Phosphorus form transformation
CN113307465A (en) * 2021-06-28 2021-08-27 天津市滨海新区环境创新研究院 River sediment habitat restoration material and preparation method thereof

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Publication number Priority date Publication date Assignee Title
JP2011173100A (en) * 2010-02-25 2011-09-08 Chugoku Electric Power Co Inc:The Granular material for water purification and water purification method
JP2012223733A (en) * 2011-04-21 2012-11-15 Hiroshima Univ Method for improving ambient water quality
CN106242214A (en) * 2016-08-22 2016-12-21 苏州科技大学 A kind of method strengthening enclosed type Sediments Endogenous Phosphorus form transformation
CN113307465A (en) * 2021-06-28 2021-08-27 天津市滨海新区环境创新研究院 River sediment habitat restoration material and preparation method thereof
CN113307465B (en) * 2021-06-28 2023-09-19 天津市滨海新区环境创新研究院 River sediment habitat restoration material and preparation method thereof

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