JP2006263509A - Method for fixing substance easily eluted in water, and material obtained by it - Google Patents
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本発明は、水に溶出し易い有害物質を同時に複数含有する焼却灰、燃焼灰、汚泥、土壌、廃棄物、排水、廃液等に反応性物質を添加することにより、該水に溶出し易い有害物質を固定化する方法、およびそれにより得られる特定用途に利用可能な資材に関する。 The present invention adds a reactive substance to incinerated ash, combustion ash, sludge, soil, waste, waste water, waste liquid, etc. that contains a plurality of harmful substances that are easily eluted in water. The present invention relates to a method for immobilizing a substance, and a material that can be used for a specific application.
焼却灰、燃焼灰、汚泥、土壌、廃棄物等、およびそれら由来の排水、廃液中には、水に溶出し易く環境に対して負荷を与える有害物質を含有することが知られている。従って、これらを環境中にそのまま排出することはできず、溶出した有害物質が環境中に放出せぬよう特別な対策を施した処理場に埋め立てるか、水に溶出し易い有害物質を難溶出性にする、即ち固定化することが行われている。ここで従来慣用に用いられている固定化処理には、固化法、化学的不溶化法、電気分解法、洗浄法および熱処理法がある。 It is known that incineration ash, combustion ash, sludge, soil, waste, etc., and wastewater and waste liquid derived from them contain harmful substances that are easily eluted into water and give a load to the environment. Therefore, they cannot be discharged into the environment as they are, and they are either buried in a treatment plant with special measures to prevent the released harmful substances from being released into the environment, or harmful substances that are likely to be dissolved in water are difficult to dissolve. In other words, fixing is performed. Conventionally used immobilization treatments include a solidification method, a chemical insolubilization method, an electrolysis method, a cleaning method, and a heat treatment method.
固化法は、被処理物をセメントまたは固化材と混合して、その表面に、さらにはその内部に遮水層を形成し、形成した遮水層により水に溶出し易い物質の短期拡散を抑制する方法である。この方法は、処理費用が安く処理能力が大きいことから広く用いられているが、長期の保存では、酸性雨によるpH変化等のために遮水層が劣化して固定化した有害物質の再溶出が起こるため、安定性が低いという欠点を有する。 In the solidification method, the material to be treated is mixed with cement or a solidified material, and a water-impervious layer is formed on the surface and further inside thereof, and the short-term diffusion of substances that easily elute into water is suppressed by the formed water-impervious layer. It is a method to do. This method is widely used because of its low processing cost and large processing capacity. However, in long-term storage, it re-elutes toxic substances that have become immobilized due to deterioration of the water shielding layer due to pH changes due to acid rain, etc. Has the disadvantage of low stability.
化学的不溶化法は、種々の化学物質を使用して、水に溶出し易い有害物質を難溶出性に変化させる方法である。水系に方法を適用する場合には、難溶性の塩を形成させて、水に溶出し易い有害物質を沈殿除去することもできる。また使用する化学物質は固定化する有害物質によって異なり、例えばカドミウムおよび鉛には水酸化物が、クロムには亜硫酸塩が、ヒ素およびセレンには鉄塩またはアルミニウム塩が、シアン化合物には次亜塩素酸ナトリウムが、ホウ素およびフッ素にはカルシウム塩またはアルミニウム塩が一般に使用される。この化学的不溶化法は処理費用が比較的安価であるため多用されるが、pH変化等により難溶出性塩が分解して再溶出が起こる虞がある。また被処理物が水に溶出し易い有害物質を複数含有する場合には、固定化する有害物質に対応して複数の化学物質を使用する必要があり、処理費用の高騰および処理作業の煩雑化を招く。 The chemical insolubilization method is a method of using various chemical substances to change a harmful substance that is easily eluted in water into a hardly soluble substance. When the method is applied to an aqueous system, it is also possible to form a hardly soluble salt and precipitate and remove harmful substances that are easily eluted in water. The chemical substances used depend on the harmful substances to be immobilized.For example, cadmium and lead are hydroxides, chromium is sulfite, arsenic and selenium are iron or aluminum salts, and cyanide is hypochlorous acid. Sodium chlorate is generally used, and calcium or aluminum salts are generally used for boron and fluorine. This chemical insolubilization method is frequently used because the processing cost is relatively low, but there is a possibility that re-elution may occur due to decomposition of a hardly soluble salt due to pH change or the like. In addition, if the material to be treated contains multiple hazardous substances that are likely to be eluted in water, it is necessary to use multiple chemical substances corresponding to the hazardous substances to be immobilized, resulting in increased processing costs and complicated processing operations. Invite.
また、水に溶出し易い有害物質の除去には、電気分解により金属イオンを回収する電気分解法、水洗および分級により濃度の高い細粒分を除去する洗浄法、並びに加熱により揮発性成分を回収する熱処理法も用いられており、これらの方法で目的物質を50%程度まで除去できる。しかしながら、それ以上の除去は困難であって多量の残留物質が生じ、また処理時間が長い、処理費用が高い等の問題もある。汚染土壌を原位置で処理する場合に行われる揚水抽出と超高圧洗浄とを組み合わせた処理においても同様の問題があり、また汚染土壌の原位置での処理では、中短期的な環境改善を目的として汚染土壌を覆砂することも行われているが、これは「臭いものに蓋」的な方法であって汚染土壌はそのまま残存するため根本的な解決には至らない。 To remove harmful substances that easily elute in water, electrolysis that recovers metal ions by electrolysis, cleaning that removes high-concentration fine particles by washing and classification, and recovery of volatile components by heating Heat treatment methods are also used, and the target substance can be removed up to about 50% by these methods. However, further removal is difficult and a large amount of residual material is generated, and there are also problems such as long processing time and high processing cost. There is a similar problem in the combined treatment of pumped water extraction and ultra-high pressure cleaning that is performed when contaminated soil is treated in situ, and in-situ treatment of contaminated soil is aimed at improving the environment in the short to medium term. As a matter of course, the contaminated soil is covered with sand, but this is a “lid on odor” method, and the contaminated soil remains as it is.
ところで、塩基性ケイ酸アルミニウムであるアロフェンは、直径約0.3〜0.5nmの微細孔を多数持つ多孔質材料である。そして、この多孔質性を利用してアロフェンは様々な物質の物理的吸着および凝集に用いられており、例えば、アロフェンに所定の配合割合で水酸化カルシウムを添加してなる浄化材が知られている(例えば、特許文献1および特許文献2参照)。この浄化材では、アロフェンと水酸化カルシウムとから合成された粘着性を有する水酸化アルミニウムと硫酸カルシウムの膜が汚水中の不純物を包み込み、アロフェンが沈殿を促進することで有害な目的物質を分離する。 Incidentally, allophane, which is basic aluminum silicate, is a porous material having a large number of fine pores having a diameter of about 0.3 to 0.5 nm. Allophane is used for physical adsorption and aggregation of various substances by utilizing this porous property. For example, a purification material obtained by adding calcium hydroxide to allophane at a predetermined blending ratio is known. (For example, see Patent Document 1 and Patent Document 2). In this purification material, a sticky aluminum hydroxide and calcium sulfate film synthesized from allophane and calcium hydroxide encloses impurities in wastewater, and allophane promotes precipitation to separate harmful target substances. .
また、ケイ素18〜24%、アルミニウム23〜29%、鉄1〜5%の化学組成を有し、アロフェンを主成分とする火山灰土壌を造粒して得られる火山灰吸着材も知られている(例えば、特許文献3参照)。これは嵩比重0.5〜0.7および水中破壊率25%以下の球状造粒物であり、ホスフィン酸イオンおよびホスホン酸イオンを吸着除去できる。 Further, a volcanic ash adsorbent having a chemical composition of 18 to 24% silicon, 23 to 29% aluminum, and 1 to 5% iron and obtained by granulating volcanic ash soil mainly composed of allophane is also known ( For example, see Patent Document 3). This is a spherical granulated product having a bulk specific gravity of 0.5 to 0.7 and an underwater destruction rate of 25% or less, and can adsorb and remove phosphinic acid ions and phosphonic acid ions.
さらに、還元性の金属と、還元剤、硫酸アルミニウム、アロフェンおよびベントナイトからなる群より選択される少なくとも1種とを含有する廃棄物処理材(例えば、特許文献4参照)、およびα化デンプンまたはデキストリンと、ケイ酸ナトリウムまたはリン酸水素塩化合物と、アロフェンとを含有する無害安定化処理剤(例えば、特許文献5参照)も知られている。ここでアロフェンは、前者では物理的吸着材として、また後者では他の2成分により生成した反応生成物の凝集材として作用する。 Furthermore, a waste treatment material containing a reducing metal and at least one selected from the group consisting of a reducing agent, aluminum sulfate, allophane and bentonite (see, for example, Patent Document 4), and pregelatinized starch or dextrin In addition, a harmless stabilizing treatment agent containing sodium silicate or hydrogen phosphate compound and allophane (for example, see Patent Document 5) is also known. Here, allophane acts as a physical adsorbent in the former and as an agglomerate of reaction products produced by the other two components in the latter.
アロフェンを用いて水中のホウ素およびフッ素を除去することも知られている(例えば、特許文献6および特許文献7参照)。この除去方法では、水中に存在するフッ素イオンまたはホウ素イオンを除去し得る成分として、アルミナ、アロフェンまたはマグネシウム化合物を択一的に使用し、また処理時には被処理水のpHを調節する必要もある。
水に溶出し易い有害物質を含み、該物質の固定化が必要な被処理物として、焼却灰の1種である石炭灰が挙げられる。この石炭灰は、エネルギー消費の増大に伴って今後も発生量が増大し続けることが予想され、発生量が多いことから処理費用が安価で処理能力が大きい方法により含まれる水に溶出し易い有害物質を固定化することが望まれている。しかしながら、従来技術でこれら2つ条件を満たす方法は固定化能力に乏しく、実用に供し得ないものであった。また石炭灰が複数の固定化すべき有害物質、例えばホウ素、フッ素、ヒ素、セレン等を同時に含有することも、処理費用の高騰および処理作業の煩雑化を招いていた。これらの理由により、有害物質の含有量が少ない一部の石炭灰が処理されているのみであって、含有量が多いものについては従来技術では十分に処理し得ず、未処理のまま埋め立てられていた。しかしながら、増え続ける石炭灰に対して埋立地の残容量は限られており、また新たな埋立地の整備も困難であることから、処理費用、処理能力および固定化能力に優れ、石炭灰処理に適用できる新規な固定化方法の開発が急務であった。 Coal ash which is a kind of incinerated ash is mentioned as a to-be-processed object which contains the harmful substance which is easy to elute in water and needs to fix | immobilize this substance. The amount of coal ash is expected to continue to increase in the future as energy consumption increases. Because of the large amount of generation, the coal ash is harmful because it is easy to elute into water contained by a method with low processing costs and high processing capacity. It is desired to immobilize the material. However, the method satisfying these two conditions in the prior art has a poor immobilization ability and cannot be put to practical use. The coal ash also contains a plurality of harmful substances to be immobilized, such as boron, fluorine, arsenic, selenium, etc., which has led to an increase in processing costs and complicated processing operations. For these reasons, only a portion of coal ash with a low content of hazardous substances has been treated, and those with a high content cannot be treated sufficiently with the prior art, and are unfilled without treatment. It was. However, the remaining capacity of landfills is limited to the increasing amount of coal ash, and it is difficult to develop new landfills. There was an urgent need to develop a new immobilization method that could be applied.
従って本発明の目的は、被処理物中に含まれる水に溶出し易い有害物質を固定化する方法であって、処理費用が安価で処理作用が容易であり、かつ固定化能力が高い方法を提供することにある。 Therefore, an object of the present invention is a method of immobilizing harmful substances that are easily eluted in water contained in the object to be treated, and is a method that is inexpensive and easy to treat, and has a high immobilization ability. It is to provide.
本発明者等は鋭意研究を行った結果、降下性火山噴出物の風化物が水に溶出し易い有害物質と結合して、難溶出性の化学的複合体を形成することを見出した。そして、この処理では、降下性火山噴出物の風化物を安価に調達でき、被処理物の増加に容易に対応可能で、固定化能力も十分であること、さらには複数の水に溶出し易い有害物質に対して同時かつ多元的に作用し得るとの知見を得て本発明を完成させた。 As a result of intensive studies, the present inventors have found that weathered products of descending volcanic products are combined with harmful substances that are easily eluted in water to form a hardly-eluting chemical complex. And in this treatment, weathered materials of descending volcanic ejecta can be procured at low cost, can easily cope with an increase in the number of objects to be treated, has sufficient immobilization ability, and is easily eluted into a plurality of waters. The present invention was completed with the knowledge that it can act simultaneously and in multiple ways against harmful substances.
さらに本発明者は、降下性火山噴出物の風化物を添加しても、添加前の被処理物の物理的性質(比重、体積、硬度、外観、強度等)に大きな影響がないことを見出した。そして、降下性火山噴出物の風化物の添加量を制御することにより、降下性火山噴出物の風化物と難溶出性の化学的複合体を形成した水に溶出し易い物質が、徐放出性を有することを利用して、該水に溶出し易い物質が極微量で存在することが有効な様々な特定の用途に、該化学的複合体を再利用し得ることをも発見した。 Furthermore, the present inventor has found that the addition of a weathering product of a descending volcanic eruption does not significantly affect the physical properties (specific gravity, volume, hardness, appearance, strength, etc.) of the object to be treated before the addition. It was. Moreover, by controlling the amount of weathering in the descending volcanic ejecta, substances that easily elute in water that forms a difficult-to-elute chemical complex with the weathering in the descending volcanic ejecta can be released slowly. It has also been discovered that the chemical complex can be reused for a variety of specific applications where it is effective that trace amounts of substances that are easily eluted in the water are present.
本発明は、降下性火山噴出物の風化物が水に溶出し易い有害物質と種々の化学的複合体を形成するという新たな知見に基き、さらに該化学的複合体の構造や組成について研究を行ってなされたものである。従って、降下性火山噴出物の風化物が1成分としてアロフェンを含有するものであったとしても、降下性火山噴出物の風化物が化学的複合体を形成することを特徴とする本発明は、アロフェンが有する多孔質構造に基いた物理的な吸着・凝集作用を利用する従来技術とは区別されるものである。 The present invention is based on the new knowledge that weathering substances of descending volcanic ejecta form various chemical complexes with harmful substances that easily elute in water, and further research on the structure and composition of the chemical complexes. It has been done. Accordingly, even if the weathered product of the descending volcanic ejecta contains allophane as one component, the present invention characterized in that the weathered product of the descending volcanic ejecta forms a chemical complex. This is different from the prior art that utilizes physical adsorption / aggregation action based on the porous structure of allophane.
即ち、本発明は、
水に溶出し易い有害物質を含有する被処理物に降下性火山噴出物の風化物を混合し、そして該混合物において該水に溶出し易い有害物質と該降下性火山噴出物の風化物との結合により難溶出性の化学的複合体を形成することを特徴とする、水に溶出し易い有害物質の固定化方法
に関する。
That is, the present invention
A weathered product of a descending volcanic eruption is mixed with an object to be treated that contains a harmful substance easily eluted in water, and a harmful substance easily eluted in the water and a weathered product of the descending volcanic ejecta in the mixture are mixed. The present invention relates to a method for immobilizing harmful substances that are easily eluted in water, characterized by forming a hardly-eluting chemical complex by binding.
本発明の水に溶出し易い有害物質の固定化方法の好ましい態様は、
前記被処理物が、焼却灰、燃焼灰、汚泥、土壌、廃棄物、排水および廃液からなる群より選択される1種または2種以上であることを特徴とする、前記水に溶出し易い有害物質の固定化方法、
前記水に溶出し易い物質が、ホウ素、フッ素、ヒ素、セレン、クロム、シアン化合物、リン、カドミウム、銅、亜鉛、鉛、水銀およびモリブデンからなる群より選択される1種または2種以上であることを特徴とする、前記水に溶出し易い有害物質の固定化方法、
前記降下性火山噴出物の風化物が、アロフェンを含有することを特徴とする、前記水に溶出し易い有害物質の固定化方法、
前記降下性火山噴出物の風化物が、粉砕および/または沈底により、20μm以下に粒度を調節したアロフェンを含有することを特徴とする、前記水に溶出し易い有害物質の固定化方法、および
前記降下性火山噴出物の風化物が、ナトリウムイオン、カリウムイオン、カルシウムイオン、マグネシウムイオン、バリウムイオン、アルミニウムイオン、鉄イオン、銅イオン、亜鉛イオンからなる群より選択される1種または2種以上の金属イオンをシラノール基に担持させたアロフェンを含有することを特徴とする、前記水に溶出し易い有害物質の固定化方法
に関する。
A preferred embodiment of the method for immobilizing a harmful substance that is easily eluted in water of the present invention is as follows.
The said to-be-processed object is 1 type, or 2 or more types selected from the group which consists of incineration ash, combustion ash, sludge, soil, waste, waste water, and waste liquid, The harmful | toxic which is easy to elute to the said water Immobilization method of substances,
The substance that easily elutes into water is one or more selected from the group consisting of boron, fluorine, arsenic, selenium, chromium, cyanide, phosphorus, cadmium, copper, zinc, lead, mercury, and molybdenum. A method for immobilizing harmful substances that easily dissolve in water,
The weathered product of the descending volcanic eruption contains allophane, the method for immobilizing harmful substances that easily dissolve in water,
The weathered product of the descending volcanic eruption product contains allophane whose particle size is adjusted to 20 μm or less by pulverization and / or sedimentation, and the method for immobilizing harmful substances easily eluted in water, The weathered product of the descending volcanic ejecta is one or more selected from the group consisting of sodium ion, potassium ion, calcium ion, magnesium ion, barium ion, aluminum ion, iron ion, copper ion and zinc ion The present invention relates to a method for immobilizing a toxic substance that easily elutes into water, comprising allophane having a metal ion supported on a silanol group.
また本発明は、
前記固定化方法により得られた難溶出性の化学的複合体を形成している水に溶出し易い有害物質と降下性火山噴出物の風化物との混合物と、セメントまたは固化剤とを含有することを特徴とする、土木用または建設用の資材に関する。
The present invention also provides
Contains a mixture of a harmful substance easily eluted in water and a weathered product of a descending volcanic eruption, and a cement or a solidifying agent, which is formed by the immobilization method and forms a hardly-eluting chemical complex. The present invention relates to a material for civil engineering or construction.
さらに本発明は、
水に溶出し易い物質を含有する被処理物に降下性火山噴出物の風化物を混合し、該混合物において該水に溶出し易い物質と該降下性火山噴出物の風化物との結合により難溶出性の化学的複合体を形成し、そして特定の用途に適する該化学的複合体を該混合物より取り出
すことを特徴とする水に溶出し易い物質の再利用方法
に関する。
Furthermore, the present invention provides
It is difficult to mix a weathered product of a descending volcanic eruption with an object to be treated that contains a material that easily dissolves in water, and it is difficult to combine the material easily eluted in the water with the weathered product of the descending volcanic ejecta. The present invention relates to a method for recycling a substance that is easily eluted in water, characterized in that it forms an eluting chemical complex and the chemical complex suitable for a particular application is removed from the mixture.
本発明の水に溶出し易い物質の再利用方法の好ましい態様は、
前記被処理物が、焼却灰、燃焼灰、汚泥、土壌、廃棄物、排水および廃液からなる群より選択される1種または2種以上であることを特徴とする、前記水に溶出し易い物質の再利用方法、
前記水に溶出し易い物質が、ホウ素、フッ素、ヒ素、セレン、クロム、シアン化合物、リン、カドミウム、銅、亜鉛、鉛、水銀およびモリブデンからなる群より選択される1種または2種以上であることを特徴とする、前記水に溶出し易い物質の再利用方法、
前記降下性火山噴出物の風化物が、アロフェンを含有することを特徴とする、前記水に溶出し易い物質の再利用方法、
前記降下性火山噴出物の風化物が、粉砕および/または沈底により、20μm以下に粒度を調節したアロフェンを含有することを特徴とする、前記水に溶出し易い物質の再利用方法、
前記降下性火山噴出物の風化物が、ナトリウムイオン、カリウムイオン、カルシウムイオン、マグネシウムイオン、バリウムイオン、アルミニウムイオン、鉄イオン、銅イオン、亜鉛イオンからなる群より選択される1種または2種以上の金属イオンをシラノール基に担持させたアロフェンを含有することを特徴とする、前記水に溶出し易い物質の再利用方法、
前記水に溶出し易い物質がホウ素であり、前記化学的複合体が次式
HOSiO3Al2(OH)2B(OH)4
で表される塩基性ケイ酸ホウ酸アルミニウムの部分構造を有し、そして該化学的複合体の組成が、モル比でSi/Al=0.1〜2.5、OH/Al=0.5〜2.9、かつSi/B=1〜2000であることを特徴とする、前記水に溶出し易い物質の再利用方法、
前記水に溶出し易い物質がフッ素であり、前記化学的複合体が次式
HOSiO3Al2(OH)2F
で表される塩基性ケイ酸フッ酸アルミニウムの部分構造を有し、そして該化学的複合体の組成が、モル比でSi/Al=0.1〜2.5、OH/Al=0.5〜2.9、かつSi/F=1〜2000であることを特徴とする、前記水に溶出し易い物質の再利用方法、
前記水に溶出し易い物質がヒ素であり、前記化学的複合体が次式
(HO)3Si3O9Al6AsO4(OH)6
で表される塩基性ケイ酸ヒ酸アルミニウムの部分構造を有し、そして該化学的複合体の組成が、モル比でSi/Al=0.1〜2.5、OH/Al=0.5〜2.9、かつSi/As=1〜2000であることを特徴とする、前記水に溶出し易い物質の再利用方法、および
前記水に溶出し易い物質がセレンであり、前記化学的複合体が次式
(HO)3Si3O9Al6SeO4(OH)6
で表される塩基性ケイ酸セレン酸アルミニウムの部分構造を有し、そして該化学的複合体の組成が、モル比でSi/Al=0.1〜2.5、OH/Al=0.5〜2.9、かつSi/Se=1〜2000であることを特徴とする、前記水に溶出し易い物質の再利用方法に関する。
A preferred embodiment of the method for reusing a substance easily eluted in water of the present invention is as follows:
The substance to be treated is one or more selected from the group consisting of incineration ash, combustion ash, sludge, soil, waste, waste water, and waste liquid, and the substance easily eluted into the water How to reuse
The substance that easily elutes into water is one or more selected from the group consisting of boron, fluorine, arsenic, selenium, chromium, cyanide, phosphorus, cadmium, copper, zinc, lead, mercury, and molybdenum. A method for reusing a substance that is easily eluted in water,
The method of reusing a substance that easily dissolves in water, characterized in that the weathered product of the descending volcanic ejecta contains allophane.
The method for reusing a substance easily eluted in water, characterized in that the weathered product of the descending volcanic eruption product contains allophane whose particle size is adjusted to 20 μm or less by pulverization and / or sedimentation,
The weathered product of the descending volcanic ejecta is one or more selected from the group consisting of sodium ion, potassium ion, calcium ion, magnesium ion, barium ion, aluminum ion, iron ion, copper ion and zinc ion A method of reusing a substance that easily dissolves in water, characterized in that it contains allophane having a metal ion supported on a silanol group,
The substance that easily elutes into water is boron, and the chemical complex has the following formula: HOSiO 3 Al 2 (OH) 2 B (OH) 4
And the composition of the chemical composite has a molar ratio of Si / Al = 0.1 to 2.5, OH / Al = 0.5. 2.9 and Si / B = 1 to 2000, the method for reusing a substance easily eluted in water,
The substance that easily elutes into water is fluorine, and the chemical complex has the following formula: HOSiO 3 Al 2 (OH) 2 F
And the chemical composite has a molar ratio of Si / Al = 0.1 to 2.5 and OH / Al = 0.5. 2.9 and Si / F = 1 to 2000, the method for reusing a substance easily eluted in water,
The substance easily eluted in water is arsenic, and the chemical complex is represented by the following formula (HO) 3 Si 3 O 9 Al 6 AsO 4 (OH) 6
And the chemical composite has a molar ratio of Si / Al = 0.1 to 2.5 and OH / Al = 0.5. 2.9 and Si / As = 1 to 2000, the method of reusing a substance easily eluted in water, and the substance easily eluted in water is selenium, and the chemical compound The body has the following formula (HO) 3 Si 3 O 9 Al 6 SeO 4 (OH) 6
And the composition of the chemical complex has a molar ratio of Si / Al = 0.1 to 2.5 and OH / Al = 0.5. It is related with the reuse method of the substance which is easy to elute in the said water characterized by being -2.9 and Si / Se = 1-2000.
加えて本発明は、前記再利用方法により得られた化学的複合体に関する。 In addition, the present invention relates to a chemical complex obtained by the recycling method.
本発明では、水に溶出し易い有害物質と火山性噴火降下物の風化物とが化学的複合体を形成するため、物理的吸着を利用する従来技術と比較して固定化能力が高い。また火山性噴火降下物の風化物は風化軽石等の原料からなり、日本中至る所で入手可能であるため安価に調達できる。さらに処理作業も被処理物に風化物を混入するだけであるので簡単に行
え、処理作業に要する時間も短く、また大量の有害物質を処理するには風化物の添加量を増大させればよいので処理量の増加にも容易に対応できる。従って本発明は、焼却灰、汚泥、建設残土等の中に含まれる有害物質の固定化に好ましく利用できる。
In the present invention, a harmful substance that easily elutes into water and a weathered product of a volcanic eruption deposit form a chemical complex, and therefore, the immobilization ability is higher than that of the conventional technique using physical adsorption. The weathered volcanic eruptions are made from raw materials such as weathered pumice and are available throughout the country, so they can be procured at low cost. Furthermore, the treatment work can be easily performed because only the weathered material is mixed into the object to be treated, the time required for the treatment work is short, and in order to treat a large amount of harmful substances, it is only necessary to increase the addition amount of the weathered material. Therefore, it can easily cope with an increase in processing amount. Therefore, the present invention can be preferably used for immobilizing harmful substances contained in incineration ash, sludge, construction residual soil, and the like.
また本発明で使用する火山性噴火降下物の風化物は、同時に複数の有害物質に対して作用して固定化し得る。これにより、個々の物質については適当な処理方法が知られていたが、複数の物質を同時に処理しようとすると処理費用が高騰したり処理作業が煩雑となるという従来技術の問題を克服でき、特に処理すべき物質を複数含有する排水、廃液等の処理に有用である。 Moreover, the weathered material of the volcanic eruption used in the present invention can be immobilized by acting on a plurality of harmful substances at the same time. As a result, an appropriate treatment method has been known for each substance, but it is possible to overcome the problems of the prior art that the treatment cost increases or the treatment work becomes complicated when trying to treat a plurality of substances at the same time. It is useful for the treatment of waste water, waste liquid, etc. containing multiple substances to be treated.
さらに本発明で使用する該火山性噴火降下物の風化物は、元より自然界に存在する地化学的物質であるため、本発明の方法により新たな環境負荷が生じることはない。また本発明では水に溶出し易い有害物質が化学的複合体を形成するので、従来のように環境の変化によって再溶出したりせず長期間安定である。これらの特徴により本発明は、汚染土壌の原位置での処理に好ましく適用できる。 Furthermore, since the weathered material of the volcanic eruption used in the present invention is a geochemical substance that is naturally present in nature, no new environmental load is caused by the method of the present invention. Further, in the present invention, since harmful substances that are easily eluted in water form a chemical complex, they are stable for a long time without being re-eluted due to environmental changes as in the prior art. Due to these characteristics, the present invention can be preferably applied to in-situ treatment of contaminated soil.
さらに本発明では、降下性火山噴出物の風化物の添加量を制御することにより、難溶出性の化学的複合体から水に溶出し易い物質が極微量ずつ放出されることを利用して、該化学的複合体を様々な用途に再利用できる。従って、本発明の化学的複合体は、特定の物質が極微量ずつ継続的に放出されることが要求される用途において、好ましく適用し得る資材となる。 Furthermore, in the present invention, by controlling the amount of weathering of the descending volcanic ejecta, it is possible to use a trace amount of substances that are easily eluted in water from a hardly-elutable chemical complex, The chemical complex can be reused for various applications. Therefore, the chemical complex of the present invention is a material that can be preferably applied in applications in which a specific substance is required to be continuously released in minute amounts.
本発明における被処理物は、降下性火山噴出物の風化物と難溶出化の化学的複合体を形成できる水に溶出し易い物質を含有するものであれば特に限定されないが、特に水に溶出し易い有害物質により汚染された物質が挙げられる。このような被処理物としては、例えば、石炭灰(フライアッシュ、クリンカアッシュ)、コークス灰、重油灰、木炭灰、スラグ等の焼却灰、燃焼灰、活性汚泥、製紙汚泥等の有機汚泥、砂利洗浄汚泥、セメント工場排水処理汚泥等の無機汚泥、建設汚泥、上下水汚泥、建設残土、重金属類等を含む汚染土壌、産業廃棄物、一般廃棄物、排水、廃液等が挙げられる。また、被処理物はこれらの2種以上の混合物であってもよい。 The material to be treated in the present invention is not particularly limited as long as it contains a substance that easily dissolves in water that can form a weathered product of descending volcanic ejecta and a chemical complex that is difficult to elute, but in particular it is eluted in water. Examples include substances that are contaminated with harmful substances that are easily treated. Examples of such materials to be treated include coal ash (fly ash, clinker ash), coke ash, heavy oil ash, charcoal ash, incinerated ash such as slag, combustion ash, activated sludge, organic sludge such as paper sludge, gravel Examples include inorganic sludge such as cleaning sludge, cement factory wastewater treatment sludge, construction sludge, water and sewage sludge, construction soil, contaminated soil containing heavy metals, industrial waste, general waste, drainage, waste liquid, and the like. Further, the object to be processed may be a mixture of two or more of these.
前記被処理物中に含まれ、前記降下性火山噴出物の風化物と化学的複合体を形成する水に溶出し易い有害物質としては、ホウ素、フッ素、砒素、セレン、クロム、シアン化合物、リン、カドミウム、銅、亜鉛、鉛、水銀、モリブデン等が挙げられる。特に近年の発生量の増大により注目される石炭灰は、ホウ素、フッ素、砒素、セレン等を含むが、従来技術では十分に難溶出化できない程にこれらを大量に含む石炭灰についても本発明は有効であり得る。また、被処理物が2種以上の水に溶出し易い物質を同時に含有する場合であっても、降下性火山噴出物の風化物は各々の物質と異なる難溶出性の化学的複合体を形成して、多元的に固定化できる。 Hazardous substances that are contained in the material to be treated and easily eluted into water that forms a chemical complex with the weathered product of the descending volcanic ejecta include boron, fluorine, arsenic, selenium, chromium, cyanide, phosphorus , Cadmium, copper, zinc, lead, mercury, molybdenum and the like. In particular, coal ash attracting attention due to an increase in the amount of generation in recent years contains boron, fluorine, arsenic, selenium, etc., but the present invention also applies to coal ash containing such a large amount that it cannot be sufficiently eluted by the prior art. Can be effective. In addition, even if the material to be treated contains two or more types of substances that are likely to elute in water, the weathered products of the descending volcanic products form a difficult-to-leach chemical complex that is different from each substance. And can be fixed in a multi-factorial manner.
本発明で使用する降下性火山噴出物の風化物は、例えば火山灰または軽石の風化物であって、成分の1つとして塩基性ケイ酸アルミニウムであるアロフェンを含有する。アロフェンは、直径約3〜5μmの微細孔を多数持つ多孔質材料であり、従来技術において物理的吸着材または凝集材として知られていた。しかしながら本発明では、降下性火山噴出物の風化物と水に溶出し易い有害物質とが化学的複合体を形成する点において、従来技術とは明らかに相違する。 The fallen volcanic eruption weathering used in the present invention is, for example, a volcanic ash or pumice weathering, and contains allophane, which is a basic aluminum silicate, as one of its components. Allophane is a porous material having a large number of fine pores having a diameter of about 3 to 5 μm, and has been known as a physical adsorbent or aggregating material in the prior art. However, the present invention is clearly different from the prior art in that the weathered material of the descending volcanic eruption and a harmful substance that easily elutes into water form a chemical complex.
また本発明では、前記降下性火山噴出物の風化物に対して粉砕または沈底を行って、前記アロフェンの粒度を調節することができる。該アロフェンの粒度は、例えば20μm以
下であり、2μmが好ましく、そして0.2μm以下が特に好ましい。
Moreover, in this invention, it grind | pulverizes or sinks with respect to the weathering thing of the said descending volcanic ejecta, and can adjust the particle size of the said allophane. The particle size of the allophane is, for example, 20 μm or less, preferably 2 μm, and particularly preferably 0.2 μm or less.
さらに前記アロフェンが有するシラノール基に金属イオンを担持させ、前記降下性火山噴出物の風化物の化学的複合体形成作用を制御することもできる。担持させる金属イオンとしては、例えば、ナトリウムイオン、カリウムイオン、カルシウムイオン、マグネシウムイオン、バリウムイオン、アルミニウムイオン、鉄イオン、銅イオン、亜鉛イオン等が挙げられ、これらのうちの1種または2種以上を担持させることができる。 Furthermore, a metal ion can be carried on the silanol group of the allophane, and the chemical complex forming action of the weathered product of the descending volcanic ejecta can be controlled. Examples of the metal ions to be supported include sodium ions, potassium ions, calcium ions, magnesium ions, barium ions, aluminum ions, iron ions, copper ions, zinc ions, etc., and one or more of these ions Can be supported.
本発明の特徴は、前記水に溶出し易い有害物質と前記降下性火山噴出物の風化物とが化学的複合体を形成することにある。該降下性火山噴出物の風化物の1成分であるアロフェンは、孔隙上に存在するSi-O-からなる部分とAl-OH2 +からなる部分とを含み、前者は鉛、銅、亜鉛、カドミウム等の陽イオンの形態を有する物質と結合し、また後者はフッ素、ホウ素、ヒ素、セレン等の陰イオンの形態を有する物質と結合してアロフェン表面上に化学的複合体を形成する。そして、一度この化学的複合体が形成すると、化学的複合体に他の陽イオンまたは陰イオンが接近してもイオン交換、配位子交換等の反応は進行せず、水に溶出し易い有害物質は難溶性のままとなる。
The feature of the present invention resides in that a harmful substance that is easily eluted in water and a weathered product of the descending volcanic ejecta form a chemical complex. Allophane, which is one component of the weathering of the descending volcanic ejecta, includes a portion made of Si—
前記化学的複合体の具体的な構造は、例えば、前記水に溶出し易い有害物質がホウ素である場合、該化学的複合体は次式
HOSiO3Al2(OH)2B(OH)4
で表される塩基性ケイ酸ホウ酸アルミニウムの部分構造を有する。そして該化学的複合体の組成は、モル比でSi/Al=0.1〜2.5、OH/Al=0.5〜2.9、かつSi/B=1〜2000であり、またその理論値はSi/Al=0.5、OH/Al=1.5、かつSi/B=2.55である。
The specific structure of the chemical complex is, for example, when the harmful substance easily eluted in water is boron, the chemical complex has the following formula: HOSiO 3 Al 2 (OH) 2 B (OH) 4
The basic aluminum silicate borate partial structure represented by these. The composition of the chemical complex is Si / Al = 0.1 to 2.5, OH / Al = 0.5 to 2.9, and Si / B = 1 to 2000 in terms of molar ratios. Theoretical values are Si / Al = 0.5, OH / Al = 1.5, and Si / B = 2.55.
また前記水に溶出し易い有害物質がフッ素である場合、前記化学的複合体は次式
HOSiO3Al2(OH)2F
で表される塩基性ケイ酸フッ酸アルミニウムの部分構造を有する。そして該化学的複合体の組成は、モル比でSi/Al=0.1〜2.5、OH/Al=0.5〜2.9、かつSi/F=1〜2000であり、またその理論値はSi/Al=0.5、OH/Al=1.5、かつSi/F=1.47である。
When the harmful substance easily eluted in water is fluorine, the chemical complex has the following formula: HOSiO 3 Al 2 (OH) 2 F
It has the partial structure of basic aluminum silicate hydrofluoric acid represented by these. The composition of the chemical complex is Si / Al = 0.1 to 2.5, OH / Al = 0.5 to 2.9, and Si / F = 1 to 2000 in molar ratios. The theoretical values are Si / Al = 0.5, OH / Al = 1.5, and Si / F = 1.47.
さらに、前記水に溶出し易い有害物質がヒ素である場合、前記化学的複合体は次式
(HO)3Si3O9Al6AsO4(OH)6
で表される塩基性ケイ酸ヒ酸アルミニウムの部分構造を有し、そして該化学的複合体の組成は、モル比でSi/Al=0.1〜2.5、OH/Al=0.5〜2.9、かつSi/As=1〜2000であり、またその理論値はSi/Al=0.5、OH/Al=1.5、かつSi/As=1.12である。
Furthermore, when the harmful substance easily eluted in water is arsenic, the chemical complex is represented by the following formula (HO) 3 Si 3 O 9 Al 6 AsO 4 (OH) 6
And the composition of the chemical complex has a molar ratio of Si / Al = 0.1 to 2.5 and OH / Al = 0.5. 2.9 and Si / As = 1 to 2000, and the theoretical values are Si / Al = 0.5, OH / Al = 1.5, and Si / As = 1.12.
同様に、前記水に溶出し易い有害物質がセレンである場合、前記化学的複合体は次式
(HO)3Si3O9Al6SeO4(OH)6
で表される塩基性ケイ酸セレン酸アルミニウムの部分構造を有し、そして該化学的複合体の組成は、モル比でSi/Al=0.1〜2.5、OH/Al=0.5〜2.9、かつSi/Se=1〜2000であり、またその理論値はSi/Al=0.5、OH/Al=1.5、かつSi/Se=1.06である。
Similarly, when the harmful substance easily eluted in water is selenium, the chemical complex has the following formula: (HO) 3 Si 3 O 9 Al 6 SeO 4 (OH) 6
And the composition of the chemical composite has a molar ratio of Si / Al = 0.1 to 2.5, OH / Al = 0.5. 2.9 and Si / Se = 1 to 2000, and the theoretical values are Si / Al = 0.5, OH / Al = 1.5, and Si / Se = 1.06.
本発明において、前記水に溶出し易い有害物質を含有する被処理物と前記降下性火山噴出物の風化物の化学的複合体は、双方を直接混練するか、または機械装置の運転過程で双方を接触させて形成できる。後者の場合、接触させる方法は混練に限定されず、従来慣用の種々の方法を使用できる。 In the present invention, the chemical complex of the object to be treated containing a harmful substance that easily elutes into water and the weathered product of the descending volcanic eruption are either directly kneaded or both in the operation process of the mechanical device. Can be formed in contact with each other. In the latter case, the contacting method is not limited to kneading, and various conventional methods can be used.
本発明の方法で処理された水に溶出し易い有害物質を含有する非処理物は、セメント、固化剤等と混合して所望の形状に成形した後、土木用資材または建設用資材として再利用できる。また本発明では、被処理物に降下性火山噴出物の風化物を添加しても、添加前の被処理物の物理的性質(比重、体積、硬度、外観、強度等)が大きく変化しないため、土木用途または建設用途に要求される特性を備えた資材を容易に得ることができる。 Non-treated materials containing harmful substances that are easily eluted in water treated by the method of the present invention are mixed with cement, solidifying agent, etc., and formed into a desired shape, and then reused as civil engineering materials or construction materials. it can. Further, in the present invention, even if a weathered product of descending volcanic ejecta is added to the object to be processed, the physical properties (specific gravity, volume, hardness, appearance, strength, etc.) of the object to be processed before the addition do not change greatly. In addition, a material having characteristics required for civil engineering or construction applications can be easily obtained.
また本発明の化学的複合体は、被処理物中の水に溶出し易い物質を難溶出性の状態で含有する。言換えると、難溶出性の該化学的複合体は、降下性火山噴出物の風化物の添加量を制御することにより、固定化した物質に、非常に微量で徐々に放出するという徐放出性を持たせることができる。従って、本発明の化学的複合体は、水に溶出し易い物質が微量ずつ継続的に放出されることが要求される用途に好ましく利用できる。このような用途の具体例として、例えば、ホウ素を含有する化学的複合体の場合には、ホウ素を必要とする職物、微生物、動物等に対する緩効性の徐放出性ホウ素肥料等、フッ素を含有する化学的複合体の場合には、ヒドロキシアパタイトを硬化する性質を利用した飲料水、歯磨き粉、練り歯磨き等のための虫歯予防剤等、またヒ素またはセレンを含有する化学的複合体の場合には、ヒ素またはセレンにより生体機能をかく乱される、細菌および鼠、野兎等のげっ歯類のための抗菌剤、殺生物剤等が挙げられる。 Further, the chemical complex of the present invention contains a substance that is easily eluted in water in the object to be treated in a hardly soluble state. In other words, the difficult-to-leach chemical complex is controlled by controlling the amount of weathering in the descending volcanic eruption, so that it is gradually released in a very small amount to the immobilized substance. Can be given. Therefore, the chemical complex of the present invention can be preferably used for an application in which a substance that is easily eluted in water is required to be continuously released in a minute amount. As a specific example of such use, for example, in the case of a chemical complex containing boron, fluorine, such as a slow-release slow-release boron fertilizer for articles, microorganisms, animals, etc. that require boron, is used. In the case of chemical complexes containing, in the case of chemical complexes containing arsenic or selenium, etc., as well as drinking water, toothpaste, toothpaste preventives for toothpaste etc. utilizing the property of curing hydroxyapatite These include antibacterial agents, biocides, and the like for rodents such as bacteria and spiders and wild birds whose biological functions are disturbed by arsenic or selenium.
以下、実施例を挙げて本発明をさらに詳しく説明するが、本発明を実施例に限定することを意図しない。 EXAMPLES Hereinafter, although an Example is given and this invention is demonstrated in more detail, it is not intending limiting this invention to an Example.
実施例1〜5および比較例1
複数の水に溶出し易い有害物質を含有する石炭灰(フライアッシュ)を被処理物として使用した。また、鳥取県倉吉で入手した大山由来の風化軽石を粉砕し、水ひによって2μm以下の粒径に調整して得た生成物を降下性火山噴出物の風化物として使用した。
上記の被処理物85gをセメント15gと混合し、得られた混合物の全重量100gに対して0.1重量%、0.5重量%、1.0重量%、5.0重量%および10重量%の添加率で降下性火山噴出物の風化物を添加した。次いで水20gを添加してこれを良く混練し、実施例1〜5の難溶出化混合物を製造した。また比較例1として、降下性火山噴出物の風化物を添加しない組成物も製造した。
Examples 1 to 5 and Comparative Example 1
Coal ash (fly ash) containing toxic substances that easily elute in a plurality of waters was used as an object to be treated. Moreover, the weathered pumice derived from Oyama obtained in Kurayoshi, Tottori Prefecture, was pulverized, and the product obtained by adjusting the particle size to 2 μm or less with hydrangea was used as a weathered product of descending volcanic ejecta.
85 g of the material to be treated is mixed with 15 g of cement, and 0.1 wt%, 0.5 wt%, 1.0 wt%, 5.0 wt% and 10 wt% with respect to 100 g of the total weight of the obtained mixture. Weathering of descending volcanic eruptions was added at a rate of% addition. Next, 20 g of water was added and this was kneaded well to produce the hardly eluting mixture of Examples 1-5. Moreover, the composition which does not add the weathering thing of a descending volcanic ejecta as the comparative example 1 was also manufactured.
こうして得られた実施例1〜5および比較例1の時被処理物について溶出試験を行った。溶出試験に際しては、予め石炭灰について従来技術のセメントによる固化法を行い、この被処理物から溶出が確認された物質:ホウ素、フッ素、ヒ素およびセレンを石炭灰中で易溶出状態にある物質であるとして試験対象元素とした。
供試体には、「セメント及びセメント系固化剤を使用した改良土の六価クロム溶出試験実施要領;国土交通省」に従って材齢7日のものを使用し、また溶出試験検液には、環境庁告示46号の方法に従って作成したものを使用した。
試験対象の測定は、ホウ素についてはJIS K 0102 47.1および47.3に、フッ素についてはJIS K 0102 34.1に、ヒ素についてはJIS K 0102 61に、またセレンについてはJIS K 0102 67.2および67.3に従って行った。
The dissolution test was performed on the objects to be processed in Examples 1 to 5 and Comparative Example 1 thus obtained. In the dissolution test, coal ash was previously solidified with cement using a conventional cement, and substances that were confirmed to be eluted from the material to be treated: boron, fluorine, arsenic, and selenium, which are easily dissolved in coal ash. As an element to be tested.
The test specimen is 7 days old according to the “Guideline for the Hexavalent Chromium Dissolution Test Using Cement and Cement-based Solidifying Agents; Ministry of Land, Infrastructure, Transport and Tourism”. The one prepared in accordance with the method of Agency Notification No. 46 was used.
The measurement of the test object is JIS K 0102 47.1 and 47.3 for boron, JIS K 0102 34.1 for fluorine, JIS K 0102 61 for arsenic, and JIS K 0102 67. for selenium. 2 and 67.3.
溶出試験結果を図1〜図4に示す。図1はホウ素の溶出試験結果を、図2はフッ素の溶出試験結果を、図3はヒ素の溶出試験結果を、また図4はセレンの溶出試験結果を示すグラフであり、各グラフにおいて、横軸は降下性火山噴出物の風化物の添加率を示し、縦軸は溶出した各元素の濃度(ppm)を示す。
図1に示されるホウ素の溶出試験結果は、降下性火山噴出物の風化物の添加率0%であるときの溶出濃度(初期溶出濃度、比較例1)が0.42ppmであったのに対し、添加
率10%(実施例5)では溶出濃度が大きく減少することを表した。また全ての実施例において、溶出濃度は環境基準である1ppm以下であった。
図2に示されるフッ素の溶出試験結果は、2.53ppmの初期溶出濃度に対して、添加率が上昇するにつれて溶出濃度が顕著に減少し、少量の添加で溶出抑制が見込めることを表した。
図3に示されるヒ素の溶出試験結果は、0.104ppmの初期溶出濃度に対して、添加率が上昇するにつれて溶出濃度が顕著に減少することを表した。
図4に示されるセレンの溶出試験結果は、0.147ppmの初期溶出濃度に対して、溶出濃度は添加率0.1%(実施例1)で既に大きく減少し、添加率10%(実施例5)では初期溶出濃度の半分の値となったことを表した。
またこれらの結果より、本発明の難溶出化混合物では4種全ての元素の溶出濃度が減少し、複数の物質を易溶出状態で含有する被処理物であっても、降下性火山噴出物の風化物の添加のみで有効に難溶出化できることを表した。
The dissolution test results are shown in FIGS. FIG. 1 shows a boron dissolution test result, FIG. 2 shows a fluorine dissolution test result, FIG. 3 shows a arsenic dissolution test result, and FIG. 4 shows a selenium dissolution test result. The axis indicates the addition rate of weathering in descending volcanic ejecta, and the vertical axis indicates the concentration (ppm) of each eluted element.
The boron elution test result shown in FIG. 1 shows that the elution concentration (initial elution concentration, Comparative Example 1) was 0.42 ppm when the weathered product addition rate of the descending volcanic ejecta was 0%. When the addition rate was 10% (Example 5), the elution concentration decreased greatly. Moreover, in all the Examples, the elution density | concentration was 1 ppm or less which is an environmental standard.
The fluorine elution test results shown in FIG. 2 showed that the elution concentration decreased significantly as the addition rate increased with respect to the initial elution concentration of 2.53 ppm, and elution suppression could be expected with a small addition.
The results of the arsenic dissolution test shown in FIG. 3 showed that the dissolution concentration markedly decreased as the addition rate increased with respect to the initial dissolution concentration of 0.104 ppm.
The results of the selenium dissolution test shown in FIG. 4 show that, with respect to the initial dissolution concentration of 0.147 ppm, the dissolution concentration is already greatly reduced at an addition rate of 0.1% (Example 1), and the addition rate is 10% (Example). 5) indicates that the value was half of the initial elution concentration.
In addition, from these results, the elution concentration of all four elements is reduced in the difficult-to-elution mixture of the present invention, and even if the object to be treated contains a plurality of substances in an elution state, It was shown that it can be effectively hardly eluted only by adding a weathered product.
Claims (21)
HOSiO3Al2(OH)2B(OH)4
で表される塩基性ケイ酸ホウ酸アルミニウムの部分構造を有し、そして該化学的複合体の組成が、モル比でSi/Al=0.1〜2.5、OH/Al=0.5〜2.9、かつSi/B=1〜2000であることを特徴とする、請求項8記載の水に溶出し易い物質の再利用方法。 The substance that easily elutes into water is boron, and the chemical complex has the following formula: HOSiO 3 Al 2 (OH) 2 B (OH) 4
And the composition of the chemical composite has a molar ratio of Si / Al = 0.1 to 2.5, OH / Al = 0.5. The method for reusing a substance easily eluted in water according to claim 8, wherein ˜2.9 and Si / B = 1 to 2000.
HOSiO3Al2(OH)2F
で表される塩基性ケイ酸フッ酸アルミニウムの部分構造を有し、そして該化学的複合体の組成が、モル比でSi/Al=0.1〜2.5、OH/Al=0.5〜2.9、かつSi/F=1〜2000であることを特徴とする、請求項8記載の水に溶出し易い物質の再利用方法。 The substance that easily elutes into water is fluorine, and the chemical complex has the following formula: HOSiO 3 Al 2 (OH) 2 F
And the chemical composite has a molar ratio of Si / Al = 0.1 to 2.5 and OH / Al = 0.5. -2.9 and Si / F = 1-2000, The recycling method of the substance which is easy to elute in water of Claim 8 characterized by the above-mentioned.
(HO)3Si3O9Al6AsO4(OH)6
で表される塩基性ケイ酸ヒ酸アルミニウムの部分構造を有し、そして該化学的複合体の組成が、モル比でSi/Al=0.1〜2.5、OH/Al=0.5〜2.9、かつSi/As=1〜2000であることを特徴とする、請求項8記載の水に溶出し易い物質の再利用方法。 The substance easily eluted in water is arsenic, and the chemical complex is represented by the following formula (HO) 3 Si 3 O 9 Al 6 AsO 4 (OH) 6
And the chemical composite has a molar ratio of Si / Al = 0.1 to 2.5 and OH / Al = 0.5. The method for reusing a substance that easily dissolves in water according to claim 8, wherein ˜2.9 and Si / As = 1 to 2,000.
(HO)3Si3O9Al6SeO4(OH)6
で表される塩基性ケイ酸セレン酸アルミニウムの部分構造を有し、そして該化学的複合体の組成が、モル比でSi/Al=0.1〜2.5、OH/Al=0.5〜2.9、かつSi/Se=1〜2000であることを特徴とする、請求項8記載の水に溶出し易い物質の再利用方法。 The substance that is easily eluted in water is selenium, and the chemical complex has the following formula (HO) 3 Si 3 O 9 Al 6 SeO 4 (OH) 6
And the composition of the chemical complex has a molar ratio of Si / Al = 0.1 to 2.5 and OH / Al = 0.5. -2.9 and Si / Se = 1-2000, The reuse method of the substance which is easy to elute in water of Claim 8 characterized by the above-mentioned.
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2011099079A (en) * | 2009-11-09 | 2011-05-19 | Fukuoka Univ | Method for producing soil conditioner, soil conditioner, and method for repairing contaminated soil by using the same |
CN102849911A (en) * | 2012-10-18 | 2013-01-02 | 黑龙江省科学院火山与矿泉研究所 | Method for passivating and repairing cadmium-polluted volcano barrier lake bottom mud |
JP2013119057A (en) * | 2011-12-07 | 2013-06-17 | Taiheiyo Materials Corp | Agent for preventing leaching of toxic substance |
JP2016077940A (en) * | 2014-10-10 | 2016-05-16 | 太平産業株式会社 | Insolubilization agent of lead in incineration ash and insolubilization method of the same |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH06184014A (en) * | 1992-12-21 | 1994-07-05 | Tokuyama Soda Co Ltd | Purification of fluorine-based inert liquid |
JPH08252564A (en) * | 1995-03-16 | 1996-10-01 | Ohbayashi Corp | Insolubilization treeatment of selenium contaminated soil |
JPH11347531A (en) * | 1998-06-10 | 1999-12-21 | Mitsubishi Materials Corp | Method for improving soil contaminated by hexavalent chromium |
JP2001219151A (en) * | 2000-02-14 | 2001-08-14 | Reio Morimoto | Waste ash sealing block body and fishing bank using the same |
JP2002263640A (en) * | 2001-03-08 | 2002-09-17 | Yamanashi Prefecture | Method of removing boron in water |
JP2002370023A (en) * | 2001-04-10 | 2002-12-24 | Kawashima Hiroaki | Adsorbent and method for adsorbing pollutant |
JP2004283760A (en) * | 2003-03-24 | 2004-10-14 | Kurita Water Ind Ltd | Method for purifying ground water |
-
2005
- 2005-03-22 JP JP2005081916A patent/JP2006263509A/en active Pending
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH06184014A (en) * | 1992-12-21 | 1994-07-05 | Tokuyama Soda Co Ltd | Purification of fluorine-based inert liquid |
JPH08252564A (en) * | 1995-03-16 | 1996-10-01 | Ohbayashi Corp | Insolubilization treeatment of selenium contaminated soil |
JPH11347531A (en) * | 1998-06-10 | 1999-12-21 | Mitsubishi Materials Corp | Method for improving soil contaminated by hexavalent chromium |
JP2001219151A (en) * | 2000-02-14 | 2001-08-14 | Reio Morimoto | Waste ash sealing block body and fishing bank using the same |
JP2002263640A (en) * | 2001-03-08 | 2002-09-17 | Yamanashi Prefecture | Method of removing boron in water |
JP2002370023A (en) * | 2001-04-10 | 2002-12-24 | Kawashima Hiroaki | Adsorbent and method for adsorbing pollutant |
JP2004283760A (en) * | 2003-03-24 | 2004-10-14 | Kurita Water Ind Ltd | Method for purifying ground water |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2011099079A (en) * | 2009-11-09 | 2011-05-19 | Fukuoka Univ | Method for producing soil conditioner, soil conditioner, and method for repairing contaminated soil by using the same |
JP2013119057A (en) * | 2011-12-07 | 2013-06-17 | Taiheiyo Materials Corp | Agent for preventing leaching of toxic substance |
CN102849911A (en) * | 2012-10-18 | 2013-01-02 | 黑龙江省科学院火山与矿泉研究所 | Method for passivating and repairing cadmium-polluted volcano barrier lake bottom mud |
JP2016077940A (en) * | 2014-10-10 | 2016-05-16 | 太平産業株式会社 | Insolubilization agent of lead in incineration ash and insolubilization method of the same |
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