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JP4832474B2 - Solidification method of soft soil using waste gypsum - Google Patents
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JP4832474B2 - Solidification method of soft soil using waste gypsum - Google Patents

Solidification method of soft soil using waste gypsum Download PDF

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JP4832474B2
JP4832474B2 JP2008176648A JP2008176648A JP4832474B2 JP 4832474 B2 JP4832474 B2 JP 4832474B2 JP 2008176648 A JP2008176648 A JP 2008176648A JP 2008176648 A JP2008176648 A JP 2008176648A JP 4832474 B2 JP4832474 B2 JP 4832474B2
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soft soil
gypsum
soil
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ettringite
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JP2010012442A (en
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秀人 蓬莱
健史 亀井
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Nikko 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
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Description

本発明は、軟弱土壌の固化処理方法に関し、特に建築廃材である廃石膏ボードを破砕・分別処理後、所定温度で加熱処理して得られる半水石膏を軟弱土壌と混合して固化処理する廃石膏を用いた軟弱土壌の固化処理方法に関する。   The present invention relates to a method for solidifying soft soil, and in particular, waste gypsum board, which is a building waste material, is crushed and separated, mixed with hemihydrate gypsum obtained by heat treatment at a predetermined temperature and solidified by mixing with soft soil. The present invention relates to a method for solidifying soft soil using gypsum.

従来、建築物の解体などに伴って多量に発生する廃石膏ボードは、そのほとんどが埋め立てなどによって廃棄処分されていたが、廃棄物処理法の改正によって廃石膏ボードが安定型産業廃棄物から管理型産業廃棄物へ移行したことに伴う処理コストの高騰や、資源の有効活用という観点からも、廃石膏ボードから石膏を分離回収して再利用することが望まれている。   Conventionally, most of the waste gypsum board that is generated in large quantities due to the dismantling of buildings has been disposed of by landfill, etc., but the waste gypsum board is managed from stable industrial waste by the revision of the Waste Disposal Law. From the viewpoint of soaring processing costs associated with the shift to industrial waste and effective utilization of resources, it is desired to separate and recover gypsum from waste gypsum board.

石膏は、結晶水の相違により二水石膏(CaSO・2HO)、半水石膏(CaSO・1/2HO)、及び無水石膏(CaSO)の三種類におおよそ分類され、二水石膏を約130℃以上に加熱処理すれば半水石膏に転位し、更に約180℃以上に加熱処理するとIII型無水石膏を経てII型無水石膏に転位する。また、半水石膏に加水処理を行うと速やかに水和反応が進んで二水石膏に転位して短時間で硬化するが、II型無水石膏に加水処理を行ってもゆっくりとしか水和反応は進まない。なお、III型無水石膏は大気中の水分を強力に吸湿するため、自然に放置しておれば極めて容易に半水石膏に転位することが判明している。 Gypsum is roughly classified into three types, dihydrate gypsum (CaSO 4 · 2H 2 O), hemihydrate gypsum (CaSO 4 · 1 / 2H 2 O), and anhydrous gypsum (CaSO 4 ). When the water gypsum is heated to about 130 ° C. or higher, it is rearranged to hemihydrate gypsum, and when it is further heated to about 180 ° C. or higher, it is transferred to type II anhydrous gypsum via type III anhydrous gypsum. In addition, when hydration treatment is performed on hemihydrate gypsum, the hydration reaction proceeds rapidly and rearranges to dihydrate gypsum and hardens in a short time. Does not advance. It has been found that type III anhydrous gypsum absorbs moisture in the atmosphere strongly, so that it can be easily converted to hemihydrate gypsum if it is allowed to stand naturally.

石膏ボードなどの石膏は二水石膏の状態にあり、これに加水処理を行っても水和反応は起こらず硬化するようなことはないが、前記のように加熱処理を施して半水石膏の状態に転位させてやれば加水処理によって短時間で硬化させることが可能となり、例えば、土壌固化材などとして十分有効的に再利用できると考えられる。   Gypsum such as gypsum board is in the form of dihydrate gypsum, and even if it is subjected to water treatment, hydration reaction does not occur and it does not harden. If it is rearranged to a state, it can be cured in a short time by water treatment, and for example, it can be reused sufficiently effectively as a soil-solidifying material.

ところが、石膏ボードの原料には火力発電所等から出される排煙脱硫石膏が多く用いられており、この排煙脱硫石膏には有害物質であるフッ素が含まれているため、回収してきた廃石膏ボードを破砕・分別処理後、所定温度で加熱処理して半水石膏としたものをそのまま土壌固化材として使用した場合には、土壌中に環境基準(0.8mg/l以下)を超える量のフッ素が溶出してしまうおそれがある。   However, flue gas desulfurization gypsum discharged from thermal power plants, etc. is often used as the raw material for gypsum board, and this flue gas desulfurization gypsum contains fluorine, which is a harmful substance. When the board is crushed and separated and then heat-treated at a predetermined temperature to produce hemihydrate gypsum as it is used as a soil-solidifying material, the amount exceeding the environmental standard (0.8 mg / l or less) in the soil Fluorine may be eluted.

上記問題に対し、例えば、特許文献1(特開2008−94901号)には、泥土固化材として使用される半水石膏に対して所定割合で酸化マグネシウムを添加することによりフッ素の溶出を抑制するようにしたものが記載されており、また特許文献2(特開2006−225475号)には、半水石膏と無水石膏とを所定の割合で配合して成る固化材を使用することによりフッ素の溶出を抑制するようにしたものが記載されている。
特開2008−94901号公報 特開2006−225475号公報
To solve the above problem, for example, Patent Document 1 (Japanese Patent Laid-Open No. 2008-94901) suppresses elution of fluorine by adding magnesium oxide at a predetermined ratio to hemihydrate gypsum used as a mud solidifying material. In addition, Patent Document 2 (Japanese Patent Application Laid-Open No. 2006-225475) describes a fluorine-containing material by using a solidifying material obtained by blending hemihydrate gypsum and anhydrous gypsum in a predetermined ratio. A product that suppresses elution is described.
JP 2008-94901 A JP 2006-225475 A

このように、廃石膏ボード等から再生した半水石膏を主成分とする土壌固化材から、フッ素が土壌中へ溶出するのを抑制するように図ったものは既に幾つか存在するが、本発明者らはこの他にも土壌固化材である半水石膏から土壌中へフッ素が溶出するのを抑制できる方法がないか検討した。   As described above, some of the soil-solidifying materials mainly composed of hemihydrate gypsum regenerated from waste gypsum board and the like have been designed to suppress the elution of fluorine into the soil. In addition to this, the inventors examined whether there is a method capable of suppressing the elution of fluorine from the hemihydrate gypsum as a soil solidifying material into the soil.

本発明は上記の点に鑑み、フッ素を含有する廃石膏ボードを破砕・加熱処理して得られる半水石膏を軟弱土壌と混合して固化処理する場合に、半水石膏中のフッ素が土壌中に溶出するのを抑制可能な廃石膏を用いた軟弱土壌の固化処理方法を提供することを課題とする。   In the present invention, in view of the above points, when hemihydrate gypsum obtained by crushing and heat-treating waste gypsum board containing fluorine is mixed with soft soil and solidified, fluorine in hemihydrate gypsum is contained in the soil. It is an object of the present invention to provide a method for solidifying soft soil using waste gypsum that can be prevented from being dissolved into the soil.

本発明者らは、上記課題を解決するために鋭意研究を重ねた結果、半水石膏に対して高炉セメントを予め所定量添加した上で軟弱土壌と混合させることにより、半水石膏から土壌中へ溶出するフッ素イオン量を抑制できることを見出した。ここで、高炉セメントはアルミナ(Al)と酸化カルシウム(CaO)成分を含有しており、これら各成分と半水石膏(CaSO・1/2HO)とが、軟弱土壌中の水分と水和反応を起こしてエトリンガイト(3CaO・Al・3CaSO・32HO)を生成し、半水石膏から溶出するフッ素イオンが前記エトリンガイトのSO 2−と置換して固定され、土壌中へのフッ素の溶出が効果的に抑制されると考えた。そして、今実験のフッ素イオンの溶出量の抑制が上記反応によるものであれば、前記高炉セメントに代えて、同様にアルミナ(Al)と酸化カルシウム(CaO)成分を含有する、例えば、高炉スラグや石炭灰等も有効に採用することが可能となり、これらは廃石膏ボードの原料である排煙脱硫石膏と同様に工業副産物であるため、環境面において好適であると共に、コストも低廉で有利であると考えられる。 As a result of intensive research to solve the above problems, the present inventors have added a predetermined amount of blast furnace cement to hemihydrate gypsum in advance and mixed it with soft soil, so that hemihydrate gypsum is mixed into the soil. It has been found that the amount of fluorine ions eluting in can be suppressed. Here, the blast furnace cement contains alumina (Al 2 O 3 ) and calcium oxide (CaO) components, and these components and hemihydrate gypsum (CaSO 4 · 1 / 2H 2 O) are contained in soft soil. causing moisture and hydration produces ettringite (3CaO · Al 2 O 3 · 3CaSO 4 · 32H 2 O), fluorine ions eluted from the hemihydrate gypsum is fixed by replacing the SO 4 2-of the ettringite It was thought that the elution of fluorine into the soil was effectively suppressed. And if suppression of the elution amount of fluorine ions in this experiment is due to the above reaction, instead of the blast furnace cement, it similarly contains alumina (Al 2 O 3 ) and calcium oxide (CaO) components, Blast furnace slag, coal ash, etc. can be used effectively, and these are industrial by-products similar to flue gas desulfurization gypsum, which is the raw material for waste gypsum board. It is considered advantageous.

また、固化処理する軟弱土壌によっては、例えば、ホウ素、ヒ素、セレン、鉛、カドミウム、クロム、水銀等、重金属を含む様々な有害物質を含有している場合があるが、これら各種有害物質のイオンについてもエトリンガイトのCa2+またはSO 2−と置換させて固定できることが文献等から判明しており、このような場合に前記固化処理を行うことで、半水石膏からの土壌中へのフッ素の溶出を抑制しながら、同時に軟弱土壌中の有害物質を浄化処理することができると考えられる。 In addition, some soft soils to be solidified may contain various harmful substances including heavy metals such as boron, arsenic, selenium, lead, cadmium, chromium and mercury. It is also known from the literature that it can be fixed by replacing it with Ca 2+ or SO 4 2- of ettringite. In such a case, by performing the solidification treatment, fluorine from the hemihydrate gypsum into the soil can be obtained. It is considered that harmful substances in soft soil can be purified while suppressing elution.

即ち、上記課題を解決するために、本発明に係る請求項1記載の廃石膏を用いた軟弱土壌の固化処理方法は、フッ素を含有する廃石膏ボードを破砕・加熱処理して得られる半水石膏を軟弱土壌と混合して固化処理する廃石膏を用いた軟弱土壌の固化処理方法において、前記半水石膏に対してアルミナと酸化カルシウムを含有する添加材として高炉セメントを所定量添加する第一の工程と、この第一の工程で添加材である高炉セメントを添加した半水石膏を軟弱土壌と混合して固化処理する第二の工程とから成り、前記第二の工程時には、半水石膏(CaSO・1/2HO)と、添加材である高炉セメントに含まれるアルミナ(Al)と酸化カルシウム(CaO)とを、軟弱土壌中の水分を利用して水和反応させてエトリンガイト(3CaO・Al・3CaSO・32HO)を生成させ、半水石膏から溶出するフッ素イオンを前記エトリンガイトのSO 2−と置換させて固定し、土壌中へのフッ素の溶出量が環境基準を超えないように抑制しながら軟弱土壌を固化処理するようにしたことを特徴としている。 That is, in order to solve the above-mentioned problem, the soft soil solidification method using waste gypsum according to claim 1 according to the present invention is a semi-water obtained by crushing and heating waste gypsum board containing fluorine. In a method for solidifying soft soil using waste gypsum in which gypsum is mixed with soft soil for solidification, a predetermined amount of blast furnace cement is added as an additive containing alumina and calcium oxide to the hemihydrate gypsum. And a second step of mixing and solidifying the hemihydrate gypsum added with the blast furnace cement as an additive in the first step with soft soil. (CaSO 4 · 1 / 2H 2 O), alumina (Al 2 O 3 ) and calcium oxide (CaO) contained in the blast furnace cement as an additive are hydrated using moisture in soft soil. Ettlingai (3CaO · Al 2 O 3 · 3CaSO 4 · 32H 2 O) is generated and the fluorine ions eluted from the hemihydrate gypsum are replaced with SO 4 2− of the ettringite and fixed, and the fluorine is eluted into the soil. It is characterized in that soft soil is solidified while suppressing the amount so as not to exceed environmental standards .

また、請求項2記載の廃石膏を用いた軟弱土壌の固化処理方法は、前記添加材として酸化カルシウム(CaO)を多く含有する高炉セメント及び/または高炉スラグと、アルミナ(Al )を多く含有する石炭灰を使用し、エトリンガイト生成にそれぞれに不足する化学成分を補填し合うようにしたことを特徴としている。 Further, solidification method soft soil with gypsum according to claim 2, wherein, as the additive, and blast furnace cement and / or blast furnace slag containing a large amount of calcium oxide (CaO), alumina (Al 2 O 3) It is characterized by using coal ash containing a large amount of ash and supplementing chemical components that are lacking in ettringite production .

また、請求項3記載の廃石膏を用いた軟弱土壌の固化処理方法は、ホウ素、ヒ素、セレン、鉛、カドミウム、クロム、水銀から選択される1種以上の有害物質を含む軟弱土壌に対し、この軟弱土壌中の前記有害物質のイオンを前記エトリンガイトのCa2+またはSO 2−と置換させて固定するようにしたことを特徴としている。 The method for solidifying soft soil using waste gypsum according to claim 3 is for soft soil containing one or more harmful substances selected from boron, arsenic, selenium, lead, cadmium, chromium and mercury. It is characterized in that the ions of the harmful substances in the soft soil are fixed by replacing the ettringite Ca 2+ or SO 4 2− .

本発明に係る請求項1記載の廃石膏を用いた軟弱土壌の固化処理方法によれば、フッ素を含有する廃石膏ボードを破砕・加熱処理して得られる半水石膏を軟弱土壌と混合して固化処理する廃石膏を用いた軟弱土壌の固化処理方法において、前記半水石膏に対してアルミナと酸化カルシウムを含有する添加材として高炉セメントを所定量添加する第一の工程と、この第一の工程で添加材である高炉セメントを添加した半水石膏を軟弱土壌と混合して固化処理する第二の工程とから成り、前記第二の工程時には、半水石膏(CaSO・1/2HO)と、添加材である高炉セメントに含まれるアルミナ(Al)と酸化カルシウム(CaO)とを、軟弱土壌中の水分を利用して水和反応させてエトリンガイト(3CaO・Al・3CaSO・32HO)を生成させ、半水石膏から溶出するフッ素イオンを前記エトリンガイトのSO 2−と置換させて固定し、土壌中へのフッ素の溶出量が環境基準を超えないように抑制しながら軟弱土壌を固化処理するようにしたので、土壌固化材として再生処理した半水石膏に含まれるフッ素が土壌中に溶出するのを抑制することができ、軟弱土壌を好適に固化処理できる。 According to the method for solidifying soft soil using waste gypsum according to claim 1 of the present invention, hemihydrate gypsum obtained by crushing and heating waste gypsum board containing fluorine is mixed with soft soil. In the method for solidifying soft soil using waste gypsum to be solidified, a first step of adding a predetermined amount of blast furnace cement as an additive containing alumina and calcium oxide to the hemihydrate gypsum, and the first step It comprises a second step in which hemihydrate gypsum added with blast furnace cement as an additive in the step is mixed with soft soil and solidified, and at the time of the second step, hemihydrate gypsum (CaSO 4 · 1 / 2H 2 O), alumina (Al 2 O 3 ) and calcium oxide (CaO) contained in the blast furnace cement , which is an additive , are hydrated using moisture in soft soil to produce ettringite (3CaO · Al 2 O). 3 · 3CaSO 4 · 32H 2 O) to generate the fluorine ions eluted from the hemihydrate gypsum is replaced with SO 4 2-of the ettringite fixed, so that the elution amount of fluorine into the soil does not exceed environmental standards Since the soft soil was solidified while restraining it, the fluorine contained in the hemihydrate gypsum regenerated as the soil solidifying material can be prevented from leaching into the soil, and the soft soil is suitably solidified. it can.

また、請求項2記載の廃石膏を用いた軟弱土壌の固化処理方法によれば、前記添加材として酸化カルシウム(CaO)を多く含有する高炉セメント及び/または高炉スラグと、アルミナ(Al )を多く含有する石炭灰を使用し、エトリンガイト生成にそれぞれに不足する化学成分を補填し合うようにしたので、添加材量を減じて処理コストを低廉に抑えることができて有利であると共に、工業副産物である高炉スラグや石炭灰を有効活用できて環境面においても有益である。 Further, according to the solidification method of soft soil with gypsum according to claim 2, as the additive, and blast furnace cement and / or blast furnace slag containing a large amount of calcium oxide (CaO), alumina (Al 2 O 3 ) Coal ash containing a large amount of ash is used to compensate for the chemical components that are deficient in ettringite formation, which is advantageous in that the amount of additive can be reduced to keep processing costs low. In addition, blast furnace slag and coal ash, which are industrial by-products, can be used effectively, which is beneficial in terms of environment.

また、請求項3記載の廃石膏を用いた軟弱土壌の固化処理方法によれば、ホウ素、ヒ素、セレン、鉛、カドミウム、クロム、水銀から選択される1種以上の有害物質を含む軟弱土壌に対し、この軟弱土壌中の前記有害物質のイオンを前記エトリンガイトのCa2+またはSO 2−と置換させて固定するようにしたので、軟弱土壌の固化処理と併せて土壌中の有害物質の浄化処理も行えて好適である。 According to the method for solidifying soft soil using waste gypsum according to claim 3, soft soil containing one or more harmful substances selected from boron, arsenic, selenium, lead, cadmium, chromium, and mercury is used. On the other hand, since the ions of the harmful substances in the soft soil are replaced with Ca 2+ or SO 4 2− of the ettringite and fixed, the purification treatment of the harmful substances in the soil is performed together with the solidification treatment of the soft soil. Can also be performed.

本発明の廃石膏を用いた軟弱土壌の固化処理方法にあっては、先ず、フッ素を含有する廃石膏ボードを所定サイズに破砕して紙類等と分別処理し、主成分である二水石膏を回収した後、この二水石膏を所定温度で加熱処理して半水石膏化し、土壌固化材として適した状態に調整する。そして、こうして得られた半水石膏に対し、アルミナ(Al)と酸化カルシウム(CaO)成分とを含有する、例えば高炉セメントや、高炉スラグ、石炭灰等の添加材を所定量添加した後、軟弱土壌と混合させて固化処理する。 In the method for solidifying soft soil using the waste gypsum of the present invention, first, the waste gypsum board containing fluorine is crushed into a predetermined size and separated from paper or the like, and dihydrate gypsum as a main component Then, the dihydrate gypsum is heat-treated at a predetermined temperature to form hemihydrate gypsum, and is adjusted to a state suitable as a soil solidifying material. Then, a predetermined amount of additives such as blast furnace cement, blast furnace slag, and coal ash containing alumina (Al 2 O 3 ) and calcium oxide (CaO) components were added to the hemihydrate gypsum thus obtained. Then, it is mixed with soft soil and solidified.

このとき、半水石膏に含まれるフッ素イオンが土壌中へと溶出しようとするが、半水石膏単独の場合と比較してその溶出量は大きく減少する。これは、半水石膏(CaSO・1/2HO)と、アルミナ(Al)、及び酸化カルシウム(CaO)が、軟弱土壌に存在する多量の水分によって水和反応を生じてエトリンガイト(3CaO・Al・3CaSO・32HO)を生成し、半水石膏から溶出するフッ素イオンを前記エトリンガイトのSO 2−と置換して固定し、土壌中へのフッ素の溶出を抑制したためと考えられる。 At this time, the fluorine ions contained in the hemihydrate gypsum try to elute into the soil, but the elution amount is greatly reduced as compared with the case of hemihydrate gypsum alone. This is due to the fact that hemihydrate gypsum (CaSO 4 · 1 / 2H 2 O), alumina (Al 2 O 3 ), and calcium oxide (CaO) undergo hydration reaction due to a large amount of moisture present in soft soil, resulting in ettringite. (3CaO · Al 2 O 3 · 3CaSO 4 · 32H 2 O) is generated, and the fluorine ions eluted from the hemihydrate gypsum are replaced with SO 4 2− of the ettringite and fixed to fix the fluorine in the soil. This is thought to be due to suppression.

このように、土壌固化材として再生処理した半水石膏に含まれているフッ素が土壌中に溶出するのを効果的に抑制することができ、環境的にも好適に軟弱土壌を固化処理できる。また、半水石膏に添加する添加材として高炉スラグや石炭灰等を採用した場合には、これらは石膏ボードの原料である排煙脱硫石膏と同様に工業副産物であるので、処理コストを比較的低廉に抑えることができると共に、これらを有効活用できることは環境面において非常に有益であると考えられる。   Thus, it is possible to effectively suppress the fluorine contained in the hemihydrate gypsum regenerated as a soil solidifying material from being eluted into the soil, and soft soil can be solidified suitably in terms of environment. In addition, when blast furnace slag, coal ash, etc. are used as additives to be added to hemihydrate gypsum, these are industrial by-products, like flue gas desulfurization gypsum, which is a raw material for gypsum board, so that the processing cost is relatively In addition to being able to keep the cost low, it is considered that it is very beneficial in terms of the environment to be able to use these effectively.

また、処理対象である軟弱土壌が、ホウ素、ヒ素、セレン、鉛、カドミウム、クロム、水銀等、重金属を含む様々な有害物質を含有している場合があるが、これら各種有害物質のイオンも同様に、前記エトリンガイトのCa2+またはSO 2−と置換させて固定させることができると考えられる。したがって、前記固化処理を施すことにより、半水石膏からのフッ素の溶出を抑制しながら、同時に土壌中の有害物質の浄化処理も行えて好適である。 In addition, the soft soil to be treated may contain various harmful substances including heavy metals such as boron, arsenic, selenium, lead, cadmium, chromium and mercury. It is considered that the ettringite can be fixed by being replaced with Ca 2+ or SO 4 2− of the ettringite. Therefore, it is preferable that the solidification treatment is performed so that the toxic substances in the soil can be purified at the same time while suppressing the elution of fluorine from the hemihydrate gypsum.

なお、エトリンガイトが有するこのような性質を積極的に利用し、例えば、フッ素を含有していない半水石膏を土壌固化材として使用する場合でも、敢えて高炉セメントや高炉スラグ、石炭灰等を添加して固化処理を行うことでエトリンガイトを生成させ、このエトリンガイトには専ら土壌中の有害物質を浄化処理させるようにしてもよい。また、固化処理を必要とするような軟弱土壌でなくとも、上記有害物質にて汚染されている土壌に対し、適宜量の半水石膏と、高炉セメントや高炉スラグ、石炭灰等を添加すると共に、水和反応に要するだけの水道水を散布することでエトリンガイトを生成させ、土壌中の有害物質を浄化処理させるといったこともできる。   In addition, by actively utilizing such properties of ettringite, for example, even when hemihydrate gypsum that does not contain fluorine is used as a soil solidifying material, blast furnace cement, blast furnace slag, coal ash, etc. are added. The ettringite may be generated by solidification treatment, and the ettringite may be subjected to purification treatment of harmful substances in the soil exclusively. Also, even if it is not soft soil that requires solidification treatment, an appropriate amount of hemihydrate gypsum and blast furnace cement, blast furnace slag, coal ash, etc. are added to the soil contaminated with the above harmful substances. It is also possible to generate ettringite by spraying tap water necessary for the hydration reaction and to purify harmful substances in the soil.

以下、本発明の一実施例を詳細に説明する。   Hereinafter, an embodiment of the present invention will be described in detail.

先ず、フッ素を含有する廃石膏ボードを細かく破砕し、紙類等と分別処理して主成分である二水石膏を回収した後、この二水石膏を約130〜180℃程度で加熱処理して半水石膏を得た。そして、固化処理する軟弱土壌の代わりに用意した、山陽クレー工業株式会社製のMCクレー(商標)100重量%に水140重量%を加えたものに対し、高炉セメントを0、5、10重量%と、前記半水石膏を0〜50重量%をそれぞれ添加して十分に攪拌混合した後、28日間養生させた。   First, the waste gypsum board containing fluorine is finely crushed and separated from paper, etc. to recover the main component dihydrate gypsum, and then the dihydrate gypsum is heated at about 130 to 180 ° C. Hemihydrate gypsum was obtained. The blast furnace cement was added to 140% by weight of water added to 100% by weight of MC clay (trademark) manufactured by Sanyo Clay Industry Co., Ltd. instead of soft soil to be solidified, and 0, 5, 10% by weight Then, 0 to 50% by weight of the hemihydrate gypsum was added and sufficiently stirred and mixed, and then cured for 28 days.

そして、前記養生後、それぞれの検体について環境庁告示第13号法に準じてフッ素の溶出試験を行い、溶出させたフッ素イオンの濃度を、水質環境基準告示付表6に掲げる方法に準じて測定し、その測定結果を図1のグラフに示す。   After the curing, each sample is subjected to a fluorine elution test in accordance with the Environmental Agency Notification No. 13 method, and the concentration of the eluted fluorine ion is measured in accordance with the method listed in Table 6 of the Water Quality Environmental Standard Notification. The measurement results are shown in the graph of FIG.

その結果、図1のグラフからも分かるように、高炉セメントを全く添加しない場合には(点線)、半水石膏の添加量に拘わらず全てフッ素の溶出量が環境基準(0.8mg/l)を超えていたのに対し、高炉セメントを5重量%(二点鎖線)または10重量%(一点鎖線)添加したものについては、フッ素の溶出量が半水石膏の添加量に拘わらず全て環境基準(0.8mg/l)を下回っていた。なお、グラフ中、半水石膏を添加しない場合においてもフッ素の溶出が認められるが、これはMCクレー中に元々含まれているフッ素によるものである。   As a result, as can be seen from the graph of FIG. 1, when no blast furnace cement is added (dotted line), the amount of fluorine elution is all environmental standards (0.8 mg / l) regardless of the amount of hemihydrate gypsum added. In contrast, for blast furnace cement with 5 wt% (double-dot chain line) or 10 wt% (single-dot chain line) added, all of the fluorine elution amount is environmental standards regardless of the amount of hemihydrate gypsum added. (0.8 mg / l). In the graph, elution of fluorine is observed even when hemihydrate gypsum is not added, but this is due to the fluorine originally contained in the MC clay.

そして、上記各検体についてエトリンガイトの存在を確認するため、各検体を粉末X線回折法により分析を行ったところ、図2に示すように、高炉セメントを添加しなかったもの(図2a)からはエトリンガイトを特定するピーク(図2aの丸で囲った部分)は見られず、エトリンガイトは生成されていなかったが、高炉セメントを5重量%または10重量%添加したもの(図2b)には何れからもエトリンガイトを特定するピーク(図2bの丸で囲った部分)が見られ、エトリンガイトの存在が確認された。   And in order to confirm presence of ettringite about each said specimen, when each specimen was analyzed by the powder X-ray diffraction method, as shown in FIG. 2, from which the blast furnace cement was not added (FIG. 2a) No peak identifying the ettringite (circled portion in FIG. 2a) was found, and no ettringite was produced, but from which blast furnace cement was added at 5% by weight or 10% by weight (FIG. 2b) In addition, a peak identifying the ettringite (circled portion in FIG. 2b) was observed, confirming the presence of ettringite.

以上の結果より、十分な水分存在下で、土壌に適宜量の半水石膏と、高炉セメント等の添加材とを添加して混合させることにより、水和反応が生じてエトリンガイトが生成され、このエトリンガイトによって半水石膏から溶出するフッ素イオンが固定され、土壌中への溶出を抑制できることが確認された。   From the above results, by adding an appropriate amount of hemihydrate gypsum and an additive such as blast furnace cement to the soil in the presence of sufficient moisture, hydration reaction occurs and ettringite is produced. It was confirmed that fluoride ions eluted from hemihydrate gypsum were fixed by ettringite and the dissolution into the soil could be suppressed.

本発明に係る廃石膏を用いた軟弱土壌の固化処理方法に関するフッ素の溶出試験の結果を示すグラフである。It is a graph which shows the result of the elution test of the fluorine regarding the solidification processing method of the soft soil using the waste gypsum concerning this invention. 本発明に係る廃石膏を用いた軟弱土壌の固化処理方法に関する粉末X線回折の結果を示す図であり、aが高炉セメントを添加しなかった場合、bが高炉セメントを添加した場合を示したものである。It is a figure which shows the result of the powder X-ray diffraction regarding the solidification processing method of the soft soil using the waste gypsum which concerns on this invention, When a did not add a blast furnace cement, b showed the case where a blast furnace cement was added. Is.

Claims (3)

フッ素を含有する廃石膏ボードを破砕・加熱処理して得られる半水石膏を軟弱土壌と混合して固化処理する廃石膏を用いた軟弱土壌の固化処理方法において、前記半水石膏に対してアルミナと酸化カルシウムを含有する添加材として高炉セメントを所定量添加する第一の工程と、この第一の工程で添加材である高炉セメントを添加した半水石膏を軟弱土壌と混合して固化処理する第二の工程とから成り、前記第二の工程時には、半水石膏(CaSO・1/2HO)と、添加材である高炉セメントに含まれるアルミナ(Al)と酸化カルシウム(CaO)とを、軟弱土壌中の水分を利用して水和反応させてエトリンガイト(3CaO・Al・3CaSO・32HO)を生成させ、半水石膏から溶出するフッ素イオンを前記エトリンガイトのSO 2−と置換させて固定し、土壌中へのフッ素の溶出量が環境基準を超えないように抑制しながら軟弱土壌を固化処理するようにしたことを特徴とする廃石膏を用いた軟弱土壌の固化処理方法。 In the method for solidifying soft soil using waste gypsum in which hemihydrate gypsum obtained by crushing and heat-treating waste gypsum board containing fluorine is mixed with soft soil, in the method for solidifying treatment of soft soil, alumina is used for the hemihydrate gypsum A first step of adding a predetermined amount of blast furnace cement as an additive containing calcium oxide, and a mixture of hemihydrate gypsum added with blast furnace cement as an additive in this first step is mixed with soft soil and solidified. It consists of a second step, wherein the time of the second step, the hemihydrate gypsum (CaSO 4 · 1 / 2H 2 O), alumina (Al 2 O 3) and calcium oxide contained in the blast furnace cement is added material ( fluorine ion to the CaO), by utilizing the moisture of soft soil by hydration reaction to produce ettringite (3CaO · Al 2 O 3 · 3CaSO 4 · 32H 2 O), eluted from hemihydrate gypsum The emissions were fixed SO 4 2-a is substituted the ettringite, characterized in that the elution amount of fluorine into the soil is such that solidification of soft soil while suppressing so as not to exceed environmental standards waste A method for solidifying soft soil using plaster. 前記添加材として酸化カルシウム(CaO)を多く含有する高炉セメント及び/または高炉スラグと、アルミナ(Al )を多く含有する石炭灰を使用し、エトリンガイト生成にそれぞれに不足する化学成分を補填し合うようにしたことを特徴とする請求項1記載の廃石膏を用いた軟弱土壌の固化処理方法。 As the additive material, and blast furnace cement and / or blast furnace slag containing a large amount of calcium oxide (CaO), using a coal ash containing a large amount of alumina (Al 2 O 3), the chemical components to be insufficient to each formation of ettringite The method for solidifying soft soil using the waste gypsum according to claim 1, wherein the soil is supplemented . ホウ素、ヒ素、セレン、鉛、カドミウム、クロム、水銀から選択される1種以上の有害物質を含む軟弱土壌に対し、この軟弱土壌中の前記有害物質のイオンを前記エトリンガイトのCa2+またはSO 2−と置換させて固定するようにしたことを特徴とする請求項1または2記載の廃石膏を用いた軟弱土壌の固化処理方法。 With respect to soft soil containing one or more kinds of harmful substances selected from boron, arsenic, selenium, lead, cadmium, chromium and mercury, ions of the harmful substances in the soft soil are converted into Ca 2+ or SO 4 2 of the ettringite. The method for solidifying soft soil using waste gypsum according to claim 1 or 2, wherein the solidified by replacing with-.
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