JP4061253B2 - Method for producing heavy metal treatment agent - Google Patents

Method for producing heavy metal treatment agent Download PDF

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JP4061253B2
JP4061253B2 JP2003308248A JP2003308248A JP4061253B2 JP 4061253 B2 JP4061253 B2 JP 4061253B2 JP 2003308248 A JP2003308248 A JP 2003308248A JP 2003308248 A JP2003308248 A JP 2003308248A JP 4061253 B2 JP4061253 B2 JP 4061253B2
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達彦 宮崎
寿彦 垣尾
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Taki Chemical Co Ltd
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本発明は、主に都市ゴミ、産業廃棄物等の焼却時に発生する焼却灰中に含有される鉛、クロム、カドミウム、水銀、銅、亜鉛あるいはニッケル等の有害重金属の安定化処理に有効な重金属処理剤及びその製造方法に関するものである。 The present invention is a heavy metal effective in stabilizing harmful heavy metals such as lead, chromium, cadmium, mercury, copper, zinc or nickel contained in incineration ash generated mainly during incineration of municipal waste, industrial waste, etc. It is related with a processing agent and its manufacturing method.

近年、都市または工場等から発生する廃棄物が増大しているが、殊に人体への悪影響が危惧される重金属を含有する廃棄物は環境対策上、十分な無害化処理が必要であり、その対策が強く要望されている。例えば都市ゴミや産業廃棄物などの焼却プラントから排出される焼却灰、特に飛灰などは鉛等の重金属を多く含むため、重金属類が溶出しないように「セメント固化法」、「酸による抽出法」、「溶融固化法」あるいは「薬剤添加処理法」のいずれかの処理を施した後、埋め立て等の最終処分をすることが義務づけられている。また平成12年1月施行のダイオキシン類対策特別措置法により規制された焼却灰中のダイオキシン類の処理についても既設の施設においては、上記4方法のうちのいずれかで処理を行う必要がある。 In recent years, waste generated from cities, factories, etc. has increased. In particular, waste containing heavy metals that are likely to have a negative impact on the human body needs to be sufficiently detoxified for environmental measures. Is strongly demanded. For example, incineration ash discharged from incineration plants such as municipal waste and industrial waste, especially fly ash, contains a lot of heavy metals such as lead. Therefore, the `` cement solidification method '' and `` acid extraction method '' prevent heavy metals from eluting. ”,“ Melt-solidification method ”, or“ Chemical addition treatment method ”, and then final disposal such as landfill is required. In addition, regarding the treatment of dioxins in incineration ash regulated by the Special Measures Law for Countermeasures against Dioxins enforced in January 2000, existing facilities need to be treated by any of the above four methods.

さて、上記処理方法中で薬剤添加処理法は他の方法に比べ、一般的に取り扱い等が簡便であることから最も多用されている。従来から用いられている薬剤として有機キレート剤があり、具体的にはジチオカルバミン酸化合物やメルカプトカルボン酸化合物などがある。しかし有機キレート剤は、高価であり処理コストが高い欠点がある。また、有機キレート剤は、pH調整用に使用する酸性薬剤と反応したり、熱い焼却灰と混合した場合、分解を起こすなどにより、硫化水素や二硫化炭素等の有害物質を生成することが報告されている。また、キレート剤は有機物であるため埋め立て処理後に、土壌の微生物によって分解されることが予想されるため、長期安定性が危惧されている。無機化合物による安定化処理方法としては、リン酸やリン酸塩化合物によって焼却灰を処理する方法が提案されているが、この方法では、処理pH範囲が限定されるため、十分な処理効果を得るためにはpH調整剤などが必要であり、また現在の規制値(鉛 0.3mg/l)をクリアするためには多くの薬剤添加量が必要となる。また、これらは酸性物質であるため装置等が腐食されやすいという欠点を有する。(例えば、特許文献1参照)   Of the above treatment methods, the drug addition treatment method is most frequently used because it is generally easier to handle than other methods. Conventionally used agents include organic chelating agents such as dithiocarbamic acid compounds and mercaptocarboxylic acid compounds. However, organic chelating agents are disadvantageous in that they are expensive and have high processing costs. In addition, organic chelating agents have been reported to produce harmful substances such as hydrogen sulfide and carbon disulfide by reacting with acidic chemicals used for pH adjustment or when decomposed when mixed with hot incineration ash. Has been. In addition, since the chelating agent is an organic substance, it is expected to be decomposed by microorganisms in the soil after the landfill treatment, and thus long-term stability is feared. As a stabilization treatment method using an inorganic compound, a method of treating incineration ash with phosphoric acid or a phosphate compound has been proposed, but this method has a sufficient treatment effect because the treatment pH range is limited. In order to achieve this, a pH adjuster or the like is required, and a large amount of drug addition is required to clear the current regulation value (lead 0.3 mg / l). In addition, since these are acidic substances, they have a drawback that the devices are easily corroded. (For example, see Patent Document 1)

また、珪酸アルミニウム等による安定化処理方法も提案されているが、同様にこれらの方法も焼却灰に対する添加量が多く必要であり、処理後の廃棄物量がかなり増加するという課題を残していた。(例えば特許文献2、3および4参照) Moreover, although the stabilization processing method by aluminum silicate etc. is also proposed, these methods similarly required much addition amount with respect to incineration ash, and the subject that the waste amount after a process increased significantly remained. (For example, see Patent Documents 2, 3, and 4)

特公平4-61710号公報Japanese Patent Publication No. 4-61710 特開平5-309354号公報JP-A-5-309354 特開平10-8029号公報Japanese Patent Laid-Open No. 10-8029 特開平11-76981号公報Japanese Patent Laid-Open No. 11-76981

本発明の目的は、上記の従来技術が有する問題点を解消するものであって、都市ゴミ、産業廃棄物等焼却時に発生する焼却灰中に含有される鉛等の各種有害重金属の安定化処理に有効な重金属処理剤に関し、高温条件下での分解による有害ガスの発生がなく、また装置の腐食が極めて少なく、かつ少ない添加量で処理できる重金属固定化能が高い重金属処理剤およびその製造方法を提供することにある。 The object of the present invention is to solve the above-mentioned problems of the prior art, and to stabilize various harmful heavy metals such as lead contained in incineration ash generated at the time of incineration such as municipal waste and industrial waste. Heavy metal treatment agent that is effective for the treatment of heavy metals, has no generation of harmful gas due to decomposition under high-temperature conditions, has very little corrosion of the device, and can be treated with a small amount of addition, and a method for producing the same Is to provide.

本発明者等は上記の課題を解決すべく鋭意検討を重ねた結果、本発明の粉体状リン酸アルミニウムシリケートからなる重金属処理剤を用いることによって、とりわけ、主灰、焼却飛灰、溶融飛灰等の焼却灰中の有害重金属が高効率で固定化されることを見いだし、本発明を完成させるに至った。即ち本発明はケイ酸ナトリウム、ケイ酸カリウム、シリカゾルから選ばれたケイ素化合物と、硫酸アルミニウム、塩化アルミニウム、硝酸アルミニウム、ポリ塩化アルミニウムから選ばれたアルミニウム化合物と、リン酸及び水溶性リン酸塩から選ばれたリン化合物とをSiO /Al モル比0.03〜3.0、P /Al モル比0.01〜1.5の範囲で混合反応させ、沈殿生成物を分離し、乾燥することを特徴とする粉体状リン酸アルミニウムシリケートからなる鉛、亜鉛、クロムから選ばれた重金属処理剤の製造方法に関する。 As a result of intensive studies to solve the above problems, the present inventors have used, among other things, main ash, incineration fly ash, molten fly by using the heavy metal treatment agent comprising the powdered aluminum phosphate silicate of the present invention. The inventors have found that harmful heavy metals in incinerated ash such as ash are fixed with high efficiency, and have completed the present invention. That is, the present invention comprises a silicon compound selected from sodium silicate, potassium silicate, and silica sol; an aluminum compound selected from aluminum sulfate, aluminum chloride, aluminum nitrate, and polyaluminum chloride; and phosphoric acid and a water-soluble phosphate. and selected phosphorous compounds SiO 2 / Al 2 O 3 molar ratio 0.03 to 3.0, by mixing and reacting in the range of P 2 O 5 / Al 2 O 3 molar ratio from 0.01 to 1.5, precipitation The present invention relates to a method for producing a heavy metal treating agent selected from lead, zinc, and chromium comprising powdered aluminum phosphate silicate, wherein the product is separated and dried .

本発明の重金属処理剤は、重金属含有廃棄物に単にこれを添加・混合するだけで有害な重金属を固定化でき、また、この重金属処理剤は、中性であるので装置の腐食がなく、かつ少ない添加量で重金属を固定化できるので、処理後の廃棄物量を大幅に低減することができる。 Heavy metal treating agent of the present invention, simply heavy metal-containing waste can immobilize only harmful heavy metals are added and mixed thereto, and the heavy metal treating agent, no corrosion of the apparatus since it is neutral, and Since heavy metals can be fixed with a small addition amount, the amount of waste after treatment can be greatly reduced.

以下、本発明に係る重金属処理剤の製造方法について詳細に説明する。本発明リン酸アルミニウムシリケートの製造方法は以下の通りである。本発明のリン酸アルミニウムシリケートは、原料としてケイ素化合物、アルミニウム化合物およびリン化合物を混合反応させて製造することができる。今、ケイ素化合物としてケイ酸ナトリウム、アルミニウム化合物として硫酸アルミニウムおよびリン化合物としてリン酸を例に挙げ具体的に説明する。 Hereinafter, the manufacturing method of the heavy metal processing agent which concerns on this invention is demonstrated in detail. The manufacturing method of this invention aluminum phosphate silicate is as follows. The aluminum phosphate silicate of the present invention can be produced by mixing and reacting a silicon compound, an aluminum compound and a phosphorus compound as raw materials. Now, sodium silicate as a silicon compound, aluminum sulfate as an aluminum compound, and phosphoric acid as a phosphorus compound will be specifically described as examples.

ケイ酸ナトリウムに、硫酸アルミニウムをSiO2/Al2O3=0.03〜3.0のモル比の範囲内で添加・混合し、次いでリン酸をP25/Al23=0.01〜1.5のモル比の範囲内で添加・混合する。得られたスラリー液のpHによって必要に応じ酸またはアルカリの中和剤で中和する。中和pHが安定化した後、得られたスラリー液を通常行われる濾過方法によって固液分離を行う。固液分離したウエットケーキを水で洗浄後、乾燥する。次いで得られたケーキ乾燥物を、粉砕することにより本発明の重金属処理剤を得ることができる。
上述したように、製造された粉体状のリン酸アルミニウムシリケートの組成は、SiO2/Al2O3=0.05〜2.6の範囲のモル比であって、且つP25/Al23=0.01〜1.2の範囲のモル比を有するものである。後記実施例で示すように、組成がこの範囲を逸脱すると重金属固定化能は著しく低下する。従って、この組成は本発明に於いては極めて重要である。今、本発明重金属処理剤の製造方法の1例を示したが、上記組成内のものであれば天然物でも使用することができる。また形態に関しては、粉体状であればよく、結晶形、無定形などどのような形態のものでも使用することができる。
Aluminum sulfate is added to sodium silicate within a molar ratio range of SiO 2 / Al 2 O 3 = 0.03 to 3.0, and then phosphoric acid is added to P 2 O 5 / Al 2 O 3 = 0.01 to 1.5 mol. Add and mix within the ratio. Depending on the pH of the obtained slurry, neutralization with an acid or alkali neutralizing agent is performed as necessary. After the neutralization pH is stabilized, the obtained slurry is subjected to solid-liquid separation by a usual filtration method. The wet cake separated into solid and liquid is washed with water and dried. Subsequently, the heavy metal processing agent of this invention can be obtained by grind | pulverizing the obtained cake dried material.
As described above, the composition of the manufactured powdery aluminum phosphate silicate has a molar ratio of SiO 2 / Al 2 O 3 = 0.05 to 2.6 and P 2 O 5 / Al 2 O 3. = Mole ratio in the range of 0.01 to 1.2. As shown in the examples described later, when the composition deviates from this range, the ability to immobilize heavy metals is significantly reduced. Therefore, this composition is extremely important in the present invention. Now, an example of the method for producing the heavy metal treating agent of the present invention has been shown, but natural products can be used as long as they are within the above composition. As for the form, it may be in the form of powder, and any form such as crystal form and amorphous form can be used.

本発明重金属処理剤の製造時の原料に関して詳述すれば、ケイ素化合物としては、ケイ酸ナトリウム、ケイ酸カリウム、シリカゾルが、アルミニウム化合物としては、硫酸アルミニウム、塩化アルミニウム、硝酸アルミニウム、ポリ塩化アルミニウムが、リン化合物としては、リン酸及び水溶性リン酸塩が好例として挙げられ、1種以上を使用できる。また、経済的、環境的観点からこれら原料を含有する廃液を利用することが推奨される。
原料であるケイ素化合物、アルミニウム化合物およびリン化合物の添加順序に関しては、特に限定されず、ケイ素化合物にアルミニウム化合物を添加し、次いでリン化合物を添加してもよく、逆にリン化合物にアルミニウム化合物を添加し、次いでケイ素化合物を添加してもよく、またアルミニウム化合物にリン化合物を添加し、次いでケイ素化合物を添加する方法などいずれの方法でも良い。また、これら3種の原料を同時に添加しても良い。
The raw materials for producing the heavy metal treating agent of the present invention will be described in detail. As the silicon compound, sodium silicate, potassium silicate, and silica sol are used. As the aluminum compound, aluminum sulfate, aluminum chloride, aluminum nitrate, and polyaluminum chloride are used. Examples of the phosphorus compound include phosphoric acid and water-soluble phosphate, and one or more of them can be used. In addition, it is recommended to use a waste liquid containing these raw materials from an economic and environmental viewpoint.
The order of addition of the silicon compound, aluminum compound, and phosphorus compound as raw materials is not particularly limited, and the aluminum compound may be added to the silicon compound, and then the phosphorus compound may be added. Conversely, the aluminum compound is added to the phosphorus compound. Then, a silicon compound may be added, or any method such as a method of adding a phosphorus compound to an aluminum compound and then adding a silicon compound may be used. These three kinds of raw materials may be added simultaneously.

本発明においては、ケイ素化合物、アルミニウム化合物およびリン化合物を反応させた後、スラリー液pHを酸またはアルカリの中和剤でpH3〜10好ましくはpH 5〜8に中和することが好ましい。中和剤としては、酸では硫酸、アルカリでは水酸化ナトリウムを用いればよい。本発明の重金属処理剤のpHを上記範囲内にすることにより、重金属固定化能は向上する。   In the present invention, after reacting the silicon compound, the aluminum compound and the phosphorus compound, it is preferable to neutralize the pH of the slurry with an acid or alkali neutralizer to pH 3 to 10, preferably pH 5 to 8. As the neutralizing agent, sulfuric acid may be used for acid, and sodium hydroxide may be used for alkali. By adjusting the pH of the heavy metal treating agent of the present invention within the above range, the heavy metal immobilization ability is improved.

次に、本発明の重金属処理剤製造過程における反応温度に関しては、反応は50℃以下、好ましくは常温近傍が最適である。反応温度が50℃以上になると重金属固定化能は低下する。しかしながら、反応完了後の中和スラリーを加熱熟成することは、すこぶる有効であり、重金属固定化能は相当向上する。この時の加熱熟成温度に関しては特段の制限はないが、設備上好ましくは沸点以下が望ましい。その熟成時間は概ね30分〜1時間程度である。
反応・中和後得られたスラリー液の濾過方法に関しては、固液分離できればどの様な分離方法を採用してもよく、例えば、遠心分離やフィルタープレス等を例示することができる。
固液分離後のウエットケーキの乾燥方法に関しては、通常の乾燥方法でよく、静置乾燥法、噴霧乾燥法等を例示することができる。また乾燥温度は、乾燥すればどの様な温度でも良いが、好ましくは150℃以下がよい。
Next, with respect to the reaction temperature in the process of producing the heavy metal treating agent of the present invention, the reaction is optimally 50 ° C. or less, preferably around room temperature. When the reaction temperature is 50 ° C. or higher, the ability to immobilize heavy metals decreases. However, heating and aging the neutralized slurry after completion of the reaction is extremely effective, and the heavy metal immobilization ability is considerably improved. Although there is no special restriction | limiting regarding the heat aging temperature at this time, Preferably it is below a boiling point on an installation. The aging time is about 30 minutes to 1 hour.
As for the filtration method of the slurry liquid obtained after the reaction / neutralization, any separation method may be adopted as long as the solid-liquid separation can be performed, and examples thereof include centrifugal separation and filter press.
Regarding the method for drying the wet cake after the solid-liquid separation, a normal drying method may be used, and a stationary drying method, a spray drying method, and the like can be exemplified. The drying temperature may be any temperature as long as it is dried, but is preferably 150 ° C. or lower.

粉砕方法に関しては、ボールミル、振動ボールミル等を例示できる。分級方法に関しては、通常の分級機、振動篩機等で行うことができる。次に、粒径に関しては、例えば焼却灰に使用する場合、焼却灰との反応性の点から、500μm以下、より好ましくは250μm以下がよい。
本発明のリン酸アルミニウムシリケートが、重金属を固定安定化する機構は明らかでないが、アルミニウムシリケートのイオン交換能、固体酸としての働きによる重金属捕捉に加えて、リン、アルミニウム、ケイ素の三成分が構造内で均一に結合することによって、新たな重金属固定安定化機構を構成しているものと推測される。これら三成分を別々に添加して用いても本発明の効果は得られない。即ち、重金属含有廃棄物に硫酸アルミニウムとケイ酸ナトリウム及びリン酸を別々に添加して処理した場合、あるいはアルミニウムシリケートとリン酸を別々に添加して処理した場合と本発明リン酸アルミニウムシリケートを添加して処理した場合とは、重金属に対する作用機構が異なるものと推測される。
Examples of the pulverization method include a ball mill and a vibration ball mill. Regarding the classification method, it can be carried out with a normal classifier, a vibration sieve or the like. Next, regarding the particle size, for example, when used for incineration ash, it is preferably 500 μm or less, more preferably 250 μm or less from the viewpoint of reactivity with incineration ash.
Although the mechanism by which the aluminum phosphate silicate of the present invention stabilizes and stabilizes heavy metals is not clear, in addition to the ion exchange capacity of aluminum silicate and the capture of heavy metals by acting as a solid acid, the three components of phosphorus, aluminum and silicon have a structure It is presumed that a new heavy metal fixation and stabilization mechanism is formed by uniformly bonding within the inside. Even if these three components are added separately, the effects of the present invention cannot be obtained. That is, when aluminum sulfate, sodium silicate and phosphoric acid are separately added to a heavy metal-containing waste and treated, or when aluminum silicate and phosphoric acid are separately added and treated, the present invention aluminum phosphate silicate is added Thus, it is presumed that the mechanism of action on heavy metals is different from the case of treatment.

次に本発明の重金属処理剤による重金属含有廃棄物の処理方法について説明する。本発明の処理剤は、単独で使用してもよく、また他の薬剤と併用しても良い。特に好ましい併用薬剤としては鉱酸、硫酸アルミニウム、活性白土、酸性白土等を例示することができる。処理方法としては、重金属含有廃棄物に本発明の重金属処理剤、併用薬剤、水を添加し、よく混練する。廃棄物への本発明の重金属処理剤、併用薬剤、水の添加順序に関しては特に限定はなく、またこれらを同時に添加してもよい。
また、これまで使用されているセメント、水ガラス、ケイ酸アルミニウム、リン酸、リン酸アルミニウム、水酸化アルミニウム、硫酸鉄、塩化鉄、キレート剤、ゼオライト、炭酸ガスなどの処理剤を本発明の効果を低下させない限り、本発明のリン酸アルミニウムシリケートと併用することを妨げるものではない。
Next, the processing method of the heavy metal containing waste by the heavy metal processing agent of this invention is demonstrated. The treatment agent of the present invention may be used alone or in combination with other drugs. Particularly preferred combination drugs include mineral acid, aluminum sulfate, activated clay, acidic clay and the like. As a treatment method, the heavy metal treatment agent of the present invention, a concomitant drug, and water are added to the heavy metal-containing waste and kneaded well. There is no particular limitation regarding the order of addition of the heavy metal treating agent of the present invention, the concomitant drug and water to the waste, and these may be added simultaneously.
In addition, the treatment agents such as cement, water glass, aluminum silicate, phosphoric acid, aluminum phosphate, aluminum hydroxide, iron sulfate, iron chloride, chelating agent, zeolite, carbon dioxide gas, etc. that have been used so far are effective in the present invention. As long as it is not lowered, it does not prevent the combined use with the aluminum phosphate silicate of the present invention.

本発明の重金属処理剤は、焼却場から発生する焼却灰等に直接添加し、上述の如く処理しても良いし、必要に応じて処理物を押し出し成形等によって成形固化させることもできる。また、酸性ガスなどを処理する煙道において使用することもできる。この場合、本発明の重金属処理剤を単独使用してもよく、また、通常煙道で使用される消石灰、活性炭などの薬剤と混合して使用しても良い。本発明の重金属処理剤を適用し得る廃棄物としては、鉛、クロム、カドミウム、水銀、銅、亜鉛あるいはニッケル等の有害重金属を含有する廃棄物であり、とりわけ上述の都市ゴミや産業廃棄物の焼却灰、殊に主灰、焼却飛灰、溶融飛灰が好例として挙げられるが、鉱滓、土壌、汚泥等に適用しても好結果を期待することができる。
以下本発明を実施例に基づいて具体的に説明するが、本発明は当該実施例のみに限定されるものではない。尚、実施例において特に断らない限り%は、全て質量%を示す。
The heavy metal treating agent of the present invention may be directly added to the incineration ash generated from the incineration site and treated as described above, or the treated product may be molded and solidified by extrusion molding or the like as necessary. Moreover, it can also be used in the flue which processes acidic gas etc. In this case, the heavy metal treating agent of the present invention may be used alone, or may be used by mixing with chemicals such as slaked lime and activated carbon usually used in a flue. The waste to which the heavy metal treating agent of the present invention can be applied is a waste containing a harmful heavy metal such as lead, chromium, cadmium, mercury, copper, zinc or nickel, and in particular, the above-mentioned municipal waste and industrial waste. Incinerated ash, particularly main ash, incinerated fly ash, and molten fly ash are listed as good examples, but good results can be expected when applied to mines, soil, sludge, and the like.
EXAMPLES Hereinafter, although this invention is demonstrated concretely based on an Example, this invention is not limited only to the said Example. In Examples, unless otherwise specified, all “%” means “% by mass”.

2Lのビーカーにケイ酸ナトリウム溶液(SiO2:28% 東曹産業株式会社製)21.5gをとり蒸留水で20倍に希釈した。その溶液中へ撹拌下で硫酸アルミニウム溶液(Al2O3:8% 多木化学株式会社製)100gを添加し、次いで85%リン酸(和光純薬株式会社製)2.9gを添加混合した。次いで20%水酸化ナトリウム溶液でpH 7に中和後、得られたスラリー液をNo.5A濾紙で濾過し蒸留水500mlで洗浄した。得られたウエットケーキを105℃の乾燥器中で12時間乾燥した。乾燥後、乳鉢で粉砕し、篩によって250μm以下に分級し重金属処理剤を得た。 In a 2 L beaker, 21.5 g of a sodium silicate solution (SiO 2 : 28% manufactured by Tosoh Sangyo Co., Ltd.) was taken and diluted 20 times with distilled water. 100 g of an aluminum sulfate solution (Al 2 O 3 : 8% manufactured by Taki Chemical Co., Ltd.) was added to the solution with stirring, and then 2.9 g of 85% phosphoric acid (manufactured by Wako Pure Chemical Industries, Ltd.) was added and mixed. Subsequently, after neutralizing to pH 7 with 20% sodium hydroxide solution, the obtained slurry was filtered with No. 5A filter paper and washed with 500 ml of distilled water. The obtained wet cake was dried in a dryer at 105 ° C. for 12 hours. After drying, the mixture was pulverized in a mortar and classified with a sieve to 250 μm or less to obtain a heavy metal treating agent.

2Lのビーカーにケイ酸ナトリウム溶液(SiO2:28%東曹産業株式会社製)14.8gをとり蒸留水で20倍に希釈した。その溶液中へ撹拌下で硫酸アルミニウム溶液(Al2O3:8%多木化学株式会社製)100gを添加し、次いで85%リン酸(和光純薬株式会社製)9.3gを添加混合した。次いで20%水酸化ナトリウム溶液でpH 7に中和後、得られたスラリー液を沸騰下で1時間加熱熟成した後、No.5A濾紙で濾過し蒸留水500mlで洗浄した。得られたウエットケーキを105℃の乾燥器中で12時間乾燥した。乾燥後、乳鉢で粉砕し、篩によって250μm以下に分級し重金属処理剤を得た。 In a 2 L beaker, 14.8 g of a sodium silicate solution (SiO 2 : 28% manufactured by Tosoh Sangyo Co., Ltd.) was taken and diluted 20 times with distilled water. 100 g of an aluminum sulfate solution (Al 2 O 3 : 8% manufactured by Taki Chemical Co., Ltd.) was added to the solution with stirring, and then 9.3 g of 85% phosphoric acid (manufactured by Wako Pure Chemical Industries, Ltd.) was added and mixed. Next, after neutralizing to pH 7 with 20% sodium hydroxide solution, the resulting slurry was heated and aged for 1 hour under boiling, then filtered through No. 5A filter paper and washed with 500 ml of distilled water. The obtained wet cake was dried in a dryer at 105 ° C. for 12 hours. After drying, the mixture was pulverized in a mortar and classified with a sieve to 250 μm or less to obtain a heavy metal treating agent.

2Lのビーカーに硫酸アルミニウム溶液(Al2O3:8%多木化学株式会社製)100gをとり、その溶液中へ撹拌下で85%リン酸(和光純薬株式会社製)5.7gを添加し、次いでケイ酸ナトリウム溶液(SiO2:28% 東曹産業株式会社製)10.9gを20倍希釈した溶液を添加混合した。次いで20%水酸化ナトリウム溶液でpH 7に中和後、得られたスラリー液をNo.5A濾紙で濾過し蒸留水500mlで洗浄した。得られたウエットケーキを105℃の乾燥器中で12時間乾燥した。乾燥後、乳鉢で粉砕し、篩によって250μm以下に分級し重金属処理剤を得た。 Take 100 g of aluminum sulfate solution (Al 2 O 3 : manufactured by Taki Chemical Co., Ltd.) in a 2 L beaker and add 5.7 g of 85% phosphoric acid (manufactured by Wako Pure Chemical Industries, Ltd.) to the solution under stirring. Then, a solution obtained by diluting 10.9 g of a sodium silicate solution (SiO 2 : 28%, manufactured by Tosoh Sangyo Co., Ltd.) 20 times was added and mixed. Subsequently, after neutralizing to pH 7 with 20% sodium hydroxide solution, the obtained slurry was filtered with No. 5A filter paper and washed with 500 ml of distilled water. The obtained wet cake was dried in a dryer at 105 ° C. for 12 hours. After drying, the mixture was pulverized in a mortar and classified with a sieve to 250 μm or less to obtain a heavy metal treating agent.

2Lのビーカーにケイ酸ナトリウム溶液(SiO2:28% 東曹産業株式会社製)2.2gをとり蒸留水で20倍に希釈した。その溶液中へ撹拌下で硫酸アルミニウム溶液(Al2O3:8% 多木化学株式会社製)100gを添加し、 次いでリン酸二水素ナトリウム・二水和物(関東化学株式会社製)7.5gを添加混合した。次いで20%水酸化ナトリウム溶液でpH 7に中和後、得られたスラリー液を、No.5A濾紙で濾過し蒸留水500mlで洗浄した。得られたウエットケーキを105℃の乾燥器中で12時間乾燥した。乾燥後、乳鉢で粉砕し、篩によって250μm以下に分級し重金属処理剤を得た。 In a 2 L beaker, 2.2 g of a sodium silicate solution (SiO 2 : 28%, manufactured by Tosoh Sangyo Co., Ltd.) was taken and diluted 20 times with distilled water. 100 g of aluminum sulfate solution (Al 2 O 3 : 8% manufactured by Taki Chemical Co., Ltd.) was added to the solution with stirring, and then sodium dihydrogen phosphate dihydrate (manufactured by Kanto Chemical Co., Ltd.) 7.5 g Were added and mixed. Then, after neutralizing to pH 7 with 20% sodium hydroxide solution, the obtained slurry was filtered with No. 5A filter paper and washed with 500 ml of distilled water. The obtained wet cake was dried in a dryer at 105 ° C. for 12 hours. After drying, the mixture was pulverized in a mortar and classified with a sieve to 250 μm or less to obtain a heavy metal treating agent.

[比較例1]
5Lのビーカーにケイ酸ナトリウム溶液(SiO2:28% 東曹産業株式会社製)61.5gをとり蒸留水で20倍に希釈した。その溶液中へ撹拌下で硫酸アルミニウム溶液(Al2O3:8% 多木化学株式会社製)100gを添加し、次いで85%リン酸(和光純薬株式会社製)2.9gを添加混合した。次いで20%水酸化ナトリウム溶液でpH 7に中和後、得られたスラリー液を、No.5A濾紙で濾過し蒸留水500mlで洗浄した。得られたウエットケーキを105℃の乾燥器中で12時間乾燥した。乾燥後、乳鉢で粉砕し、篩によって250μm以下に分級し重金属処理剤を得た。
[Comparative Example 1]
In a 5 L beaker, 61.5 g of sodium silicate solution (SiO 2 : 28% manufactured by Tosoh Sangyo Co., Ltd.) was taken and diluted 20 times with distilled water. 100 g of an aluminum sulfate solution (Al 2 O 3 : 8% manufactured by Taki Chemical Co., Ltd.) was added to the solution with stirring, and then 2.9 g of 85% phosphoric acid (manufactured by Wako Pure Chemical Industries, Ltd.) was added and mixed. Then, after neutralizing to pH 7 with 20% sodium hydroxide solution, the obtained slurry was filtered with No. 5A filter paper and washed with 500 ml of distilled water. The obtained wet cake was dried in a dryer at 105 ° C. for 12 hours. After drying, the mixture was pulverized in a mortar and classified with a sieve to 250 μm or less to obtain a heavy metal treating agent.

[比較例2]
5Lのビーカーにケイ酸ナトリウム溶液(SiO2:28%東曹産業株式会社製)0.17gをとり蒸留水で20倍に希釈した。その溶液中へ撹拌下で硫酸アルミニウム溶液(Al2O3:8%多木化学株式会社製)100gを添加し、次いで85%リン酸(和光純薬株式会社製)11.2g添加混合した。次いで20%水酸化ナトリウム溶液でpH 7に中和後、得られたスラリー液を、No.5A濾紙で濾過し蒸留水500mlで洗浄した。得られたウエットケーキを105℃の乾燥器中で12時間乾燥した。乾燥後、乳鉢で粉砕し、篩によって250μm以下に分級し重金属処理剤を得た。
[Comparative Example 2]
In a 5 L beaker, 0.17 g of a sodium silicate solution (SiO 2 : 28%, manufactured by Tosoh Sangyo Co., Ltd.) was taken and diluted 20 times with distilled water. 100 g of an aluminum sulfate solution (Al 2 O 3 : 8% manufactured by Taki Chemical Co., Ltd.) was added to the solution with stirring, and then 11.2 g of 85% phosphoric acid (manufactured by Wako Pure Chemical Industries, Ltd.) was added and mixed. Then, after neutralizing to pH 7 with 20% sodium hydroxide solution, the obtained slurry was filtered with No. 5A filter paper and washed with 500 ml of distilled water. The obtained wet cake was dried in a dryer at 105 ° C. for 12 hours. After drying, the mixture was pulverized in a mortar and classified with a sieve to 250 μm or less to obtain a heavy metal treating agent.

[比較例3]
5Lのビーカーにケイ酸ナトリウム溶液(SiO2:28% 東曹産業株式会社製)16.0gをとり蒸留水で20倍に希釈した。その溶液中へ撹拌下で硫酸アルミニウム溶液(Al2O3:8% 多木化学株式会社製)100gを添加混合した。次いで20%水酸化ナトリウム溶液でpH 7に中和後、得られたスラリー液を、No.5A濾紙で濾過し蒸留水500mlで洗浄した。得られたウエットケーキを105℃の乾燥器中で12時間乾燥した。乾燥後、乳鉢で粉砕し、篩によって250μm以下に分級し重金属処理剤を得た。
「重金属処理試験」
実施例1〜4及び比較例1〜3で得られた重金属処理剤を蛍光X線装置を使用して分析を行ない、SiO2/Al2O3(モル比) 及びP25/Al23(モル比)を求めた。結果を表1に示す。
[Comparative Example 3]
In a 5 L beaker, 16.0 g of sodium silicate solution (SiO 2 : 28% manufactured by Tosoh Sangyo Co., Ltd.) was taken and diluted 20 times with distilled water. 100 g of an aluminum sulfate solution (Al 2 O 3 : 8% manufactured by Taki Chemical Co., Ltd.) was added and mixed into the solution under stirring. Then, after neutralizing to pH 7 with 20% sodium hydroxide solution, the obtained slurry was filtered with No. 5A filter paper and washed with 500 ml of distilled water. The obtained wet cake was dried in a dryer at 105 ° C. for 12 hours. After drying, the mixture was pulverized in a mortar and classified with a sieve to 250 μm or less to obtain a heavy metal treating agent.
"Heavy metal treatment test"
The heavy metal treating agents obtained in Examples 1 to 4 and Comparative Examples 1 to 3 were analyzed using a fluorescent X-ray apparatus, and SiO 2 / Al 2 O 3 (molar ratio) and P 2 O 5 / Al 2 were analyzed. O 3 (molar ratio) was determined. The results are shown in Table 1.

Figure 0004061253
Figure 0004061253

上記組成の重金属処理剤を用いて焼却飛灰を処理し、重金属の溶出試験を行った。使用した焼却飛灰は、K市ゴミ処理場の焼却飛灰(Pb 0.15%、Zn 0.66%、Cr 110ppm;Pb溶出量31.7mg/l)であり、焼却飛灰の溶出試験は、上記焼却飛灰に対し実施例及び比較例で得られた重金属処理剤を15%、水を30%添加し、混練した後、昭和48年環境庁告示第13号記載の方法で溶出試験を行った。溶出試験結果を表2に示す。
上記重金属処理剤以外に、比較例4として試薬珪酸アルミニウム(米山薬品工業株式会社製、Al2O3・3SiO2)を上記と同様の割合で使用した場合及び比較例5として85%リン酸溶液(和光純薬製、試薬特級)を上記と同様の割合で使用した場合の結果を、また比較例6として比較例3の重金属処理剤10%と85%リン酸6%を併用した場合(SiO2/Al2O3=0.95、P25/Al23=0.53)の結果も併せて表2に示す。
また、実施例5としてA市ゴミ焼却場の焼却飛灰(Pb 0.10%、Zn 0.43%、Cr 60ppm;Pb溶出量:18.2mg/l)に、実施例3の重金属処理剤を添加した場合の溶出試験結果も表2に示す。
Incineration fly ash was treated with a heavy metal treating agent having the above composition, and a heavy metal elution test was conducted. The incineration fly ash used was the incineration fly ash (Pb 0.15%, Zn 0.66%, Cr 110ppm; Pb elution amount 31.7mg / l) at the K City garbage treatment plant. After 15% of the heavy metal treating agent obtained in Examples and Comparative Examples and 30% of water were added to the ash and kneaded, the dissolution test was conducted by the method described in Notification No. 13 of the Environment Agency in 1973. The dissolution test results are shown in Table 2.
In addition to the above heavy metal treating agent, the reagent aluminum silicate (manufactured by Yoneyama Pharmaceutical Co., Ltd., Al 2 O 3 · 3SiO 2 ) is used as Comparative Example 4 in the same proportion as above and 85% phosphoric acid solution as Comparative Example 5 (Wako Pure Chemicals, reagent grade) results when used in the same proportion as above, and as Comparative Example 6 when 10% of the heavy metal treatment agent of Comparative Example 3 and 85% phosphoric acid 6% are used together (SiO 2 / Al 2 O 3 = 0.95, P 2 O 5 / Al 2 O 3 = 0.53) are also shown in Table 2.
In addition, in Example 5, the heavy metal treatment agent of Example 3 was added to the incineration fly ash (Pb 0.10%, Zn 0.43%, Cr 60ppm; Pb elution amount: 18.2 mg / l) at the A municipal waste incineration plant. The dissolution test results are also shown in Table 2.

Figure 0004061253
Figure 0004061253

表2に示す溶出試験結果から明らかなように、同じ粉体状リン酸アルミニウムシリケートであっても組成が極めて重要であり、本発明の重金属処理剤を用いて処理すれば容易に鉛の埋立基準である鉛溶出量を0.3ppm以下にすることができる。鉛以外の重金属については、いずれの実施例においてもZn1ppm以下、Cr0.05ppm以下の溶出量であった。これにより本発明の重金属処理剤は鉛等有害な重金属を含有する廃棄物に対して有効であることが確認された。 As is apparent from the dissolution test results shown in Table 2, the composition is extremely important even with the same powdery aluminum phosphate silicate, and it is easily treated with the heavy metal treatment agent of the present invention for lead landfill standards. The lead elution amount can be reduced to 0.3 ppm or less. As for heavy metals other than lead, the elution amounts were Zn 1 ppm or less and Cr 0.05 ppm or less in any of the examples. Thereby, it was confirmed that the heavy metal processing agent of this invention is effective with respect to the waste containing harmful heavy metals, such as lead.

本発明の重金属処理剤は、リン酸アルミニウムシリケートからなり、有害な重金属を含有する廃棄物、とりわけ焼却灰を処理した場合、重金属固定化能に優れ、例えば容易に鉛の埋立基準である鉛溶出量を0.3ppm以下にすることができるため、重金属含有廃棄物の無害化処理に非常に有効なものである。
The heavy metal treatment agent of the present invention is composed of aluminum phosphate silicate, and is excellent in heavy metal immobilization ability when treating waste containing harmful heavy metals, especially incineration ash, for example, lead elution, which is the standard for lead reclamation. Since the amount can be reduced to 0.3 ppm or less, it is very effective for detoxifying heavy metal-containing waste.

Claims (2)

ケイ酸ナトリウム、ケイ酸カリウム、シリカゾルから選ばれたケイ素化合物と、硫酸アルミニウム、塩化アルミニウム、硝酸アルミニウム、ポリ塩化アルミニウムから選ばれたアルミニウム化合物と、リン酸及び水溶性リン酸塩から選ばれたリン化合物とをSiOA silicon compound selected from sodium silicate, potassium silicate, and silica sol; an aluminum compound selected from aluminum sulfate, aluminum chloride, aluminum nitrate, and polyaluminum chloride; and phosphorus selected from phosphoric acid and water-soluble phosphate Compound with SiO 2 /Al/ Al 2 O 3 モル比0.03〜3.0、PMolar ratio 0.03-3.0, P 2 O 5 /Al/ Al 2 O 3 モル比0.01〜1.5の範囲で混合反応させ、沈殿生成物を分離し、乾燥することを特徴とする粉体状リン酸アルミニウムシリケートからなる鉛、亜鉛、クロムから選ばれた重金属処理剤の製造方法。Heavy metal treatment selected from lead, zinc, and chromium consisting of powdered aluminum phosphate silicate characterized by mixing and reacting in a molar ratio of 0.01 to 1.5, separating and drying the precipitated product Manufacturing method. 重金属が、都市ゴミ焼却灰または産業廃棄物焼却灰に含まれる重金属である請求項1記載の重金属処理剤の製造方法The method for producing a heavy metal treatment agent according to claim 1, wherein the heavy metal is a heavy metal contained in municipal waste incineration ash or industrial waste incineration ash.
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