JP2009001961A - Hydrophilic property improving method for tideland in river having accumulated sludge and hydrophilic soil structural material used in the method - Google Patents

Abstract

<P>PROBLEM TO BE SOLVED: To improve the hydrophilic property of a tideland in a river by utilizing the soil, which is obtained by dredging or the mud on its bottom dug up for a percolation column produced when restoring the tideland, as a sand covering material for making effective use of waste and restore the improved tideland so as to obtain such firmness that allows a person to walk on the tideland at the same time. <P>SOLUTION: In this hydrophilic property improving method for the tideland, a stream of river water is formed between an underground sand layer and a surface layer in the river rs, the percolation column 1 made of lime ash granulated particulates is inserted into the riverbed rb and the tideland rf where organic mud is accumulated to supply oxygen into the mud accumulated on the riverbed rb, and the soil dug up when drilling an intrusion hole 3 at the construction work site when inserting the percolation column 1 is mixed with the lime ash granulated particulates to produce the hydrophilic soil structural material, which is spread all over the tideland rf in which the percolation column 1 is inserted as the sand covering material 2. <P>COPYRIGHT: (C)2009,JPO&INPIT

Description

  The present invention relates to a technique for repairing tidal flats in rivers, and in particular, sludge using a hydrophilic sand-covering material mixed with sludge such as dredged soil, sludge and coal ash granulated material generated during river restoration accumulates. The present invention relates to a method for improving hydrophilicity of river tidal flats and a hydrophilic soil structure material used therefor.

  In the river tidal flat developed in the tidal river area, organic mud transported from the sea area rises and sinks due to the tide not only upstream but also from the sea area. When organic mud accumulates on tidal flats, it becomes difficult for sludge to flow down, and further sludge formation progresses. As a result, the water circulation within the sediment is hindered, the accumulation of nutrients, the accumulation of harmful substances such as sulfides, etc., the river purification capacity is reduced, and the living habitat of the organism is deteriorated. In addition, the landscape value of the waterside in the river tidal flat is also reduced.

  Examples of such environmental purification measures for river tidal flats include dredging and large-scale sand cover. However, dredging mud accumulation continues, disposal of dredged soil and runoff of sprayed sand cover, etc., and establishment of new sediment mud countermeasure technology is required.

For example, to prevent sludge formation in river tidal flats, spraying sand-covering material on the mud of tidal flat bottom or the surface of the tidal flat has been proposed, and technology that uses purification materials such as zeolite and activated carbon as the sand-covering material has been proposed. Yes. The present applicant has already filed a patent application for Japanese Patent Application No. 2005-369095 “Artificial Tidal Flat Formation Method for Establishing Tidal Flats in the Estuary or Coastal Area” of Patent Document 1. This tidal flat construction method is an artificial tidal flat construction method that creates artificial tidal flats in the estuary or coastal area, and mud soil such as dredged soil is buried in the tidal flat construction section in the estuary or coastal area. Next, coal ash granulate is laid on the upper layer of the lower landfill layer to form a coal ash granulated layer, and mud is further buried on the upper layer of the coal ash granulated layer. The upper landfill layer is formed, and the coal ash granulated material is formed in a substantially columnar shape (penetration column) in the upper landfill layer, and a plurality of these are arranged in a staggered pattern or a lattice shape. In this method, the entire surface of the landfill soil layer is covered with sand covering so as to have a predetermined thickness.
Japanese Patent Application No. 2005-369095

In addition, as a technique for effectively using dredged bottom mud, as shown in Japanese Patent Application Laid-Open No. 2003-268745, “Artificial tidal flat and its creation method”, a mixture of organic matter and a sandy material is mixed. It is an artificial tidal flat constructed using a construction material. By making the chemical oxygen demand (COD) of the construction material 2 to 15 mg per 1 g of dry weight, it is excellent in the effect of purifying soil and water quality and the effect of biological growth. It is possible to effectively use dredged soil, or materials mixed with organic matter such as waste generated in the aquaculture business or food manufacturing process, and to create an artificial tidal flat that does not require the supply of clean sand or sandy soil from the outside. Technology has been proposed.
JP 2003-268745 A

In addition, as shown in Japanese Patent Application Laid-Open No. 2004-49933 “Method for treating dredged mud”, the mud deposited on the bottom of the water is dredged, and then the dredged mud is separated into sand and sand, and then the mud that has been separated into sand and sand is separated. In order to dewater dredged mud soil by laying a cloth formwork on the bottom of the coastal area of the sea, lakes, etc., and filling the cloth formwork with the primary dewatering cake generated by the centrifugation. There is proposed a technique for treating dredged mud to prevent the progress of water contamination without having to secure a site for disposal of the dehydrated cake and the dehydrated cake, and effectively utilizing the dehydrated cake generated at that time.
JP 2004-49933 A

  However, the conventional spraying of sand-capping material on the tidal flats is a countermeasure only for the surface of the tidal flats, not a drastic restoration of river tidal flats. River tidal flats that have only been sprayed with conventional sand-capping material have not been restored to a level that allows people to walk. Also, disposal of dredged clay has become difficult year after year.

  The inventor of the present invention has paid attention to the fact that dredged soil generated in a large amount during restoration of river tidal flats and bottom mud excavated when embedding the infiltration column in the implementation of the creation method of Patent Document 1. For example, we focused on restoring this river tidal flat so that it can be used as a staircase structure at the dock. In river tidal flats where there are rocky areas, we focused on forming a tide pool that would allow a tide pool to be created when it was submerged. In addition, we focused on the fact that slopes can be formed in rivers with high banks.

  The technique of patent document 2 is an artificial tidal flat excellent in the effect of purifying soil and water quality and the effect of biological growth, which is a construction material obtained by mixing an organic substance-mixed material and a sandy material. However, the dredged soil and the bottom mud excavated when embedding infiltration columns were not used effectively during the restoration of river tidal flats.

  Although the technique of the said patent document 3 uses the dewatering cake of harbor dredging mud as a mat-like formation, there existed a problem that the water quality and mud quality could not be efficiently restored in the artificially constructed tidal flat.

  The present invention has been developed to solve such problems. That is, the object of the present invention is to improve the hydrophilicity of the tidal flat by effectively using waste by using the dredged soil generated during the restoration of river tidal flats or the bottom mud excavated for infiltration columns as the sand covering material. It is another object of the present invention to provide a method for improving the hydrophilicity of a river tidal flat where sludge accumulates and the hydrophilic soil structure material used therefor, which can be repaired to such a degree that the modified tidal flat can be walked.

According to the restoration method of the present invention, a method for improving the hydrophilicity of a river tidal flat (rf) in which sludge accumulates in the river (rs), the river between the underground sand layer and the surface layer in the river (rs) In order to form a flow of water and supply oxygen into the sedimentary mud in the river bed (rb), an infiltration column (coal ash granulated material) is formed on the riverbed (rb) and the tidal flat (rf) where the organic mud is deposited ( 1), the excavated soil excavated when opening the penetration hole (3) in the work site when penetrating the penetration column (1) is mixed with the coal ash granulated material to make a hydrophilic soil structure A river in which sludge accumulates, characterized in that a material is produced and used as a sand-capping material (2), and the sand-covering material (2) is spread on a tidal flat (rf) penetrating the infiltration column (1). A method for improving the hydrophilicity of tidal flats is provided.
Or, at the work site where the river is being restored, the sludge drowned in the purification of the river is mixed with the coal ash granulated material to produce a hydrophilic soil structure material, which is used as the sand covering material (2), The sand-capping material (2) can be spread on the tidal flat (rf) penetrating the infiltration column (1).

  Calcium contained in the osmotic column (1) can be obtained by using hydrolyzed and pressure-molded coal ash generated from a coal-fired power plant of the pressurized fluidized bed combined power generation system for the osmotic column (1). It is preferable to react with phosphorus contained in the organic mud of the river tidal flat (rf) to generate and fix stable hydroxyapatite. It is preferable to use a sand mixed material (2) mixed with sand.

According to the hydrophilic soil structure material of the present invention, the infiltration column (1) made of coal ash granule is penetrated into the river bed (rb) and the tidal flat (rf) in the river (rs), and the infiltration column (1). A hydrophilic soil structure material spread on a tidal flat (rf) penetrating the river, wherein the hydrophilic soil structure material is a mixture of coal ash granulated material and excavated soil excavated during restoration of a river (rs) There is provided a hydrophilic soil structure material used for improving the hydrophilicity of a river tidal flat characterized by
Or the said hydrophilic earth structure material can mix the sludge produced when drowning in the restoration | repair of a river with the coal ash granulated material.

  For example, the coal ash granulated material is obtained by hydrolyzing and pressure-molding coal ash generated from a pressurized fluidized bed combined power generation type coal-fired power plant.

In the method for improving hydrophilicity of the present invention, the coal ash granule is mixed with excavated soil or sludge to produce a hydrophilic soil structure material, which is used as a sand-capping material (2), and a large number of penetration columns (1) are formed. By spreading on the intruded tidal flat (rf), the drainage of the tidal flat (rf) can be improved and the adsorption characteristics of phosphorus can be improved. For example, the mud flats (rf) can be restored to a hardness that allows people to walk.
The coal ash granulated material mixed in the permeation column (1) and the hydrophilic sand-capping material (2) has the ability to fix phosphorus, so that it can not only repair the mud but also is contained in the mud. It has the function of suppressing the elution of phosphorus into water by immobilizing phosphorus and restoring the water quality.
In particular, since the excavated soil or dredged sludge mixed with the coal ash granulated material is generated in the work site where the river (rs) is being repaired, The amount of generation can be reduced and the tidal flat (rf) can be repaired quickly.

  By carrying out the method for improving hydrophilicity of the present invention, the hydrophilicity of the river (rs) can be improved, and the waterfront environment such as improvement of water quality / bottom quality in the river (rs) is improved. In addition, by restoring the tidal flat (rf) to a level that allows people to walk, the riverside walkway (promenade) can connect people and the waterfront. For example, even in rivers (rs) where water taxis were conventionally available only at high tide, the restored tidal flats (rf) can also be used for boarding at low tides.

  The hydrophilic earth structure material (hydrophilic sand-clad material (2)) of the present invention is made of coal ash (PFBC ash) generated from a pressurized fluidized bed combined power generation type coal-fired power plant as a main material for improving the hydrophilicity. Coal ash, which is industrial waste, is effectively used, and the use of this material leads to a reduction in environmental burden.

  The method for improving the hydrophilicity of a river tidal flat where sludge is deposited according to the present invention is obtained by mixing a coal ash granulated material with dredged soil or a bottom mud excavated for an infiltrating column during restoration of a river tidal flat. This is a method to improve the hydrophilicity of river tidal flats by spreading it over riverbeds and tidal flats as sand-capping material.

Hereinafter, preferred embodiments of the present invention will be described with reference to the drawings.
FIG. 1 is a schematic cross-sectional view illustrating a method for improving the hydrophilicity of a river tidal flat where sludge accumulates in Example 1 of the present invention. FIG. 2 is a schematic plan view illustrating a method for improving the hydrophilicity of a river tidal flat where sludge is deposited according to the first embodiment. FIG. 3 is a flowchart showing a method for improving the hydrophilicity of a river tidal flat where sludge accumulates in Example 1.
In the method for improving the hydrophilicity of a river tidal flat where sludge accumulates in Example 1 of the present invention, first, a large number of infiltrated columns 1 made of coal ash granulated material are inserted into the riverbed rb and tidal flat rf where organic mud is deposited. At the work site when penetrating the seepage pillar 1, the excavated soil excavated when the penetration hole 3 is opened is mixed with coal ash granulated material to produce a hydrophilic soil structure material, which is covered with the sand covering material 2. Lay down on the tidal flat rf.

  For the permeation column 1, for example, hydrolyzed and pressure-molded coal ash (PFBC ash) generated from a coal-fired power plant using a pressurized fluidized bed combined power generation system is used. The calcium contained in the permeation column 1 has a function of reacting with phosphorus contained in the river bed rb of the river rs or the organic mud of the tidal flat rf to generate and fix stable hydroxide apatite. This can restore muddy and water quality and improve the hydrophilicity of river tidal flats.

  As shown in FIG. 2, a plurality of the permeation pillars 1 are arranged in a tidal flat rf in a staggered pattern or a lattice pattern with a predetermined interval. Flow of river water is formed between the underground sand layer and the surface layer of river rs or tidal flat rf via infiltration column 1 due to fluctuations in water pressure due to tides, tidal currents and waves. Can be supplied with oxygen. Therefore, oxygen can be supplied to the mud to improve the environment suitable for living organisms.

  In the method for improving the hydrophilicity of a river tidal flat where sludge accumulates in Example 1, the excavated soil excavated when opening the penetration hole 3 is mixed with the coal ash granulated material at the work site for penetrating the infiltration column 1. Thus, the sand covering material 2 is generated. In this way, at the work site where the river is being restored, the generated excavated soil is mixed with coal ash granulated material to produce a hydrophilic soil structure material, which is used as the sand-capping material 2 for construction disposal. The generation amount of objects can be reduced, and the tidal flat rf can be repaired quickly.

  The hydrophilic soil structure material (sand covering material 2) generated at the work site where the river is being restored is spread over the tidal flat rf and the river bed rb so as to have a predetermined thickness. As shown in FIGS. 1 and 2, the sand covering material 2 is spread at a position higher than the low water level. Since the present invention does not aim only at improving the water quality, it needs to be hard enough for a person to stand and walk on the sand covering material 2. The sand covering material 2 is preferably used by further mixing sand.

  By spreading the mixed sand-clad material 2 mixed in this manner on the tidal flat rf, the drainage of the tidal flat rf can be improved, and the phosphorus adsorption property can be improved. For example, the mud flats rf can be restored to a hardness that allows people to walk. The coal ash granulate has the ability to fix phosphorus, so that it can not only repair muddy matter, but also can fix phosphorus contained in the mud and suppress elution of phosphorus into the water, thereby restoring water quality. Can be planned.

  The river tidal flat restored in this way can be used as a staircase-like structure at the dock, that is, a tree. Unlike the quay, this wall can be lifted and loaded regardless of whether the water surface is up or down due to tides or river flow changes.

  In the river tidal flat rf where there is a rocky area, a tide pool can be formed where tides can be accumulated when the tide is lowered, and in this tide pool, river play and river creatures can be observed. In addition, the tidal flat rf of the river with a high bank is repaired to form a ramp, and it is possible to further drive cars and bicycles on this ramp.

  By carrying out the hydrophilicity improving method of the present invention, the hydrophilicity of the river rs can be improved, and the waterfront environment such as improvement of water quality / bottom quality in the river rs is improved. The riverside walkway connects people with the water. For example, even in a river where a water taxi has been conventionally available only at high tide, the restored tidal flat rf can also be used as a water taxi boarding at low tide.

  The hydrophilic soil structure material of the present invention does not restrict the habitat of organisms such as crabs, and even in tidal flats where sludge is accumulated, in order to improve the hardness to a level that can be walked, It can be used as a temporary collapse / overflow.

  The hydrophilic earth structure material of the present invention can be actively used as a construction material for a promenade, a terrace, a tide pool or the like in the river rs.

  As described above, the hydrophilic soil structure material (sand covering material 2) of the present invention can be used together with the permeation column 1 to improve the environmental repair effect and hydrophilicity of the river rs. As a result, waterside playgrounds, water traffic start points, waterside cafes, etc. can be developed, and regional promotion through multipurpose use of watersides can be improved. The hydrophilic soil structure material is a material having both hardness and softness in combination with various waterside spaces. If necessary, it is collapsed and swept back to natural sedimentation in case of emergency such as flood. The hydrophilicity improvement method using this hydrophilic earth structure material is made into the required intensity | strength and structure form according to a place to be used and a use. In addition, considering the relationship between people and river flow in river rs and the landscape, and installing promenades, terraces, tide pools, etc. in appropriate places, it can respond to river environmental conditions such as different environmental aspects and economic aspects at each point. The optimal environmental restoration work that has been made possible.

FIG. 4 is a flowchart showing a method for improving the hydrophilicity of a river tidal flat where sludge accumulates in Example 2.
The method for improving the hydrophilicity of river tidal flats in which sludge accumulates in Example 2 is basically the same as the method for improving hydrophilicity in Example 1, but when generating a hydrophilic soil structure material (sand cover material 2). It is characterized by mixing sludge drowned during river purification into coal ash granulation. This is a hydrophilicity improvement method that can also utilize sludge with a riverbed rb or the like when a predetermined amount of the intended hydrophilic soil structure is insufficient in the amount of excavated soil of the seepage column. Thus, in combination with the permeation column 1, the drainage of the tidal flat rf and the river bed rb is improved by spreading the hydrophilic sand-clad material 2 in which sludge is mixed with the coal ash granule on the tidal flat rf, and the phosphorus adsorption characteristics are improved. Can be improved.

  As described above, in the method for improving the hydrophilicity of river tidal flats where sludge is deposited according to the present invention, materials such as excavated soil and dredged soil, which are environmental loads if not used, are effectively used.

  Furthermore, with the method for improving the hydrophilicity of river tidal flats where sludge accumulates according to the present invention, the development of new businesses such as water traffic and the increase in the amount of useful bivalve molluscs such as swordfish and clams dramatically improve the fishery value of river channels Can be expected. Moreover, the direct economic effect is limited by the method for improving the hydrophilicity of river tidal flats where this sludge is deposited, but the secondary economic effect by the restoration of the water environment is extremely large.

FIG. 5 is a plan view showing a river in which the method for improving hydrophilicity of a river tidal flat where sludge is deposited according to the present invention is implemented.
The situation where the method for improving the hydrophilicity of a river tidal flat where sludge is deposited according to the present invention is actually implemented in the river rs will be described. In the illustrated example, the tidal flat rf had a length of 110 m and a width of 8 m, the construction range of the permeation column 1 was 880 m ² , and the number of constructions of the permeation column 1 was 370. Moreover, the laying range of the sand-capping material 2 of the present invention was 400 m ² . The construction method used was a cylindrical half bucket type excavation method. Construction was carried out in the river by work platform 4 and material platform 5. Note that the symbol b in the illustrated example is a bridge.

  As shown in Table 1, the physical properties of the coal ash granulated material mixed with the permeation column 1 or the hydrophilic sand-capping material 2 are those of general river sand (density, internal friction angle, hydraulic conductivity). ) And almost the same value. Moreover, the density is smaller than the density of general sand because there are many voids inside the hardened coal ash that constitutes the granulated product, and this is aerobic that purifies the organic mud of the tidal flat rf. It works to provide a good habitat for the microbial community.

  As described above, the coal ash (PFBC ash) constituting the coal ash granule contains abundant calcium, and is contained in the organic mud of the calcium and the tidal flat rf and the main component of the pollution load source in the water area. It reacts with element phosphorus to produce stable hydroxyapatite and fix it. It can be said that the coal ash granule is involved in water quality restoration in the water area from such chemical properties.

The main construction contents at each construction stage are, as shown in the flowchart of FIG. 3, first, as “preparation work”, there are correspondences related to ceremonies and navigation of the work platform 4 and various procedures.
Next, as “penetration column installation work”, the location of the penetration column 1 is located, the removal of the boulders at the location of the penetration column 1 is excavated, the excavation by the dedicated excavator for laying the penetration column 1, and the packing of coal ash granules The penetration column 1 is inserted into the penetration hole 3.
“Sand-covering” means local production of sand-capping material 2 mixed with excavated soil, coal ash granulated material and river sand, laying in a predetermined thickness of sand-capping material 2 with a predetermined thickness and manual sand-capping There is.
Lastly, the finished shape inspection / completion includes confirmation of the number, diameter and depth of the penetrating pillars 1, confirmation of the thickness of the sand covering material 2, laying range, dismantling of the work platform 4 and rounding.

Furthermore, in order to confirm the effect of river tidal flat restoration, the mud quality and biota of the tidal flat before and after the installation of this environmental restoration work will be confirmed.
[Survey period]
The river tidal flat survey should be conducted in the summer when the river environment is most deteriorating. In addition, the effect confirmation after the installation of the environmental restoration works will be conducted at the same time as the current survey period.
[Investigation position]
The river tidal flat state survey location is set to the miouji location to measure the water level and water temperature of the tidal flat rf and river rs near the area where the environmental restoration works are installed. In the environmental restoration work area, the place where the hydrophilic sand-capping material 2 is present and the place where the hydrophilic sand-covering material 2 is absent are set as the investigation positions.
[Method and contents of monitoring]
As shown in Table 2, the contents of monitoring measurements conducted prior to the implementation of the environmental restoration works are as follows. Conduct bottom sediment survey and biological survey of tidal flat rf. At the same time, a trap survey will be conducted to investigate suspended solids accumulated in river tidal flats. There shall be one survey site.

  In the environmental repair area, as described above, measurement is performed at two places, where the sand covering material 2 is present and where it is not present. Table 3 shows the survey contents in the environmental restoration area. The water level, DO, salinity, and water temperature sensors are installed inside the infiltration column 1, and the influence on each measurement item due to the water flow generated inside the infiltration column 1 due to the installation of the infiltration column 1 is continuous (for 3 months). Observe at. On the sand-capping material 2, the ground support force and the soil color are observed.

For the permeation column 1, the physical and chemical properties of the mud that are assumed to be affected as a result of the permeation flow occurring in the surrounding mud layer due to the water flow generated inside the permeation column 1 Measure. At the same time, a trap survey is conducted to investigate the suspended matter accumulated in the tidal flat rf of the river rs in the same manner as in the current situation survey, and the change in suspended matter due to the difference in the presence or absence of environmental restoration work is grasped.
As a comparison, a current state survey will be conducted at the same time.

  The present invention uses the dredged soil generated during the restoration of the river tidal flat rf or the bottom mud excavated for the seepage pillar 1 for the sand-capping material 2, thereby effectively utilizing the waste to make the hydrophilicity of the tidal flat rf. However, the present invention is not limited to the above-described embodiment and can be variously modified without departing from the gist of the present invention. It is.

  As described above, according to the method for improving the hydrophilicity of river tidal flats on which sludge accumulates according to the present invention and the hydrophilic soil structure material used therefor, it can also be used for a tidal flat construction project for repairing tidal flats.

It is a schematic sectional drawing explaining the hydrophilicity improvement method of the river tidal flat where the sludge of Example 1 accumulates. It is a schematic plan view explaining the hydrophilicity improvement method of the river tidal flat where the sludge of Example 1 accumulates. It is a flowchart which shows the hydrophilicity improvement method of the river tidal flat where the sludge of Example 1 accumulates. It is a flowchart which shows the hydrophilicity improvement method of the river tidal flat where the sludge of Example 2 accumulates. It is a top view which shows the river which implemented the hydrophilicity improvement method of the river tidal flat where the sludge of this invention accumulates.

Explanation of symbols

1 Infiltration pillar 2 Sand-capping material (hydrophilic soil structure material)
3 Penetration hole 4 Work trolley 5 Material trolley rs River rb River bed rf Tidal flat b Bridge

Claims (7)

A method for improving the hydrophilicity of a river tidal flat that repairs a tidal flat (rf) where sludge accumulates in the river (rs),
In order to form a stream of river water between the underground sand layer and the surface layer in the river (rs) and supply oxygen into the sedimentary mud in the river bed (rb), the river bed (rb) and tidal flat ( rf) penetrates the permeation column (1) made of coal ash granulation,
At the work site when penetrating the penetration column (1), the excavated soil excavated when opening the penetration hole (3) is mixed with coal ash granulated material to produce a hydrophilic soil structure material, To cover sand (2)
A method for improving the hydrophilicity of a river tidal flat where sludge accumulates, characterized in that the sand covering material (2) is spread over a tidal flat (rf) penetrating the infiltration column (1). A method for improving the hydrophilicity of a river tidal flat that repairs a tidal flat (rf) where sludge accumulates in the river (rs),
In order to form a stream of river water between the underground sand layer and the surface layer in the river (rs) and supply oxygen into the sedimentary mud in the river bed (rb), the river bed (rb) and tidal flat ( rf) penetrates the permeation column (1) made of coal ash granulation,
At the work site where the river is being restored, the sludge drowned in the purification of the river is mixed with coal ash granulated material to produce a hydrophilic soil structure material, which is used as sand-capping material (2),
A method for improving the hydrophilicity of a river tidal flat where sludge accumulates, characterized in that the sand-capping material (2) is spread on a tidal flat (rf) penetrating the infiltration column (1). Calcium contained in the osmotic column (1) can be obtained by using hydrolyzed and pressure-molded coal ash generated from a coal-fired power plant of the pressurized fluidized bed combined power generation system for the osmotic column (1). 3. Improvement of hydrophilicity of river tidal flat where sludge accumulates, characterized by reacting phosphorus contained in organic mud of river tidal flat (rf) to generate and fix stable hydroxyapatite Method. The method for improving the hydrophilicity of a river tidal flat where sludge is deposited according to claim 1 or 2, wherein the sand-capping material (2) is a mixture of sand. Hydrophilic soil that penetrates the infiltration column (1) made of coal ash granulated material into the river bed (rb) and tidal flat (rf) in the river (rs) and spreads over the tidal flat (rf) that has penetrated the infiltration column (1) A structural material,
In order to improve the hydrophilicity of a river tidal flat, the hydrophilic soil structure material is a mixture of coal ash granulated material and excavated soil excavated during restoration of a river (rs) Hydrophilic soil structure material to be used. Hydrophilic soil that penetrates the infiltration column (1) made of coal ash granulated material into the river bed (rb) and tidal flat (rf) in the river (rs) and spreads over the tidal flat (rf) that has penetrated the infiltration column (1) A structural material,
In order to improve the hydrophilicity of a river tidal flat characterized in that the hydrophilic soil structure material is a mixture of coal ash granulated material and sludge generated when dredging during river restoration Hydrophilic soil structure material to be used. The river tidal flat according to claim 5 or 6, wherein the coal ash granulated material is obtained by adding water and press molding coal ash generated from a coal-fired power plant of a pressurized fluidized bed combined power generation system. Hydrophilic soil structural material used to improve the hydrophilicity of the material.

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