JP2008264627A - Waste treatment material and treatment method for detoxifying fly ash (soot and dust) and burned ash or the like - Google Patents
Waste treatment material and treatment method for detoxifying fly ash (soot and dust) and burned ash or the like Download PDFInfo
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Abstract
Description
本発明は産業廃棄物や都市ごみの焼却施設から排出される有害重金属(鉛、カドミウム、銅、亜鉛あるいはクロムなど)を含んだ飛灰(ばいじん)や焼却灰などを無害化、(不溶出化)する廃棄物処理薬材及び無害化処理方法に関する。 The present invention renders fly ash (dust) and incineration ash containing hazardous heavy metals (lead, cadmium, copper, zinc, chromium, etc.) discharged from incineration facilities of industrial waste and municipal waste harmless (non-eluting) The present invention relates to a waste treatment chemical and a detoxification treatment method.
産業廃棄物や都市ごみの焼却施設から排出される有害重金属を含んだ飛灰(ばいじん)や焼却炉を無害化(不溶出化)できる薬剤として有機液体キレート薬剤が一般的に用いられている。(特許文献1,2および3)しかし有機液体キレートは飛灰(ばいじん)や焼却灰と混合、混練して処理する際に人体に有害な二硫化炭素(化学式:CS2)や硫化水素(化学式:H2S)やアンモニア(化学式:NH3)やアミン類(化学式:R-NH2)などの臭気成分ガスを発生する。また、貯蔵時に有害臭気成分ガスが発生するなどして危険である。したがって、換気設備などの安全装置を完備しなければならないなど設備費が高価になる。 Organic liquid chelating agents are generally used as agents capable of detoxifying (non-eluting) fly ash (dust) containing hazardous heavy metals discharged from industrial waste and municipal waste incineration facilities. (Patent Documents 1, 2 and 3) However, organic liquid chelates are mixed with kneaded fly ash and incinerated ash, kneaded and processed, and carbon disulfide (chemical formula: CS 2 ) and hydrogen sulfide (chemical formula) are harmful to the human body. : H 2 S), ammonia (chemical formula: NH 3 ), amines (chemical formula: R—NH 2 ) and other odorous component gases are generated. Also, it is dangerous because harmful odor component gas is generated during storage. Therefore, the equipment cost becomes expensive, for example, a safety device such as a ventilation facility must be provided.
その他、有機液体キレート薬剤で飛灰(ばいじん)や焼却炉を無害化(不溶出化)した処理物は、埋立処分場へ搬入されて埋め立てられる。 In addition, processed ash that has been rendered harmless (non-eluting) with organic liquid chelating agents is transported to a landfill site and landfilled.
有機液体キレート薬剤で、無害化(不溶出化)された飛灰(ばいじん)や焼却灰は埋立処分場で長期間埋め立てられた後に無酸素状態(嫌気状態)での微生物や菌によって分解されて、不溶出化された処理物に含有される有害重金属が再溶出してくる。 Detoxified (non-eluting) fly ash and incineration ash by organic liquid chelating agents are decomposed by microorganisms and fungi in anoxic (anaerobic) condition after being landfilled for a long time at a landfill site. The harmful heavy metals contained in the non-eluting treatment product are re-eluted.
本発明は無機粉末の廃棄物処理材で人体に有害な臭気成分ガスの発生しない、あるいは埋立処分場で長期間埋立てられても微生物や菌によって分解されない処理方法を提供する。 The present invention provides a treatment method that does not generate odorous component gas harmful to human body with an inorganic powder waste treatment material or that is not decomposed by microorganisms or fungi even if it is landfilled for a long time in a landfill site.
本発明の周辺技術としては粉末状のアルミニウムシリケートまたは粉体状二酸化ケイ素(特許文献4参照)やX線的に非晶質な水酸化アルミニウム20重量%以上95重量%以下と粉体状の多孔質無機吸着剤および/または水溶性燐酸塩5重量パーセント以上と80重量%以下とを含み、かつ前記X線的に非晶質を水酸化アルミニウムと粉体状の多孔質無機吸着剤および/または水溶性リン酸塩との合計量が50重量%以上である廃棄物処理剤(特許文献5参照)などが挙げられるがいずれも無機粉体状廃棄物処理剤で原材料を数種類混合しなければならず用途が限定されるなどの問題がある。 Peripheral techniques of the present invention include powdered aluminum silicate or powdered silicon dioxide (see Patent Document 4) or X-ray amorphous aluminum hydroxide in an amount of 20% to 95% by weight and powdery porous material. Inorganic adsorbent and / or water-soluble phosphate 5 wt% or more and 80 wt% or less, and said X-ray amorphous aluminum hydroxide and powdery porous inorganic adsorbent and / or Examples include waste treatment agents with a total amount of water-soluble phosphate of 50% by weight or more (see Patent Document 5). In any case, several types of raw materials must be mixed with inorganic powder waste treatment agents. There are problems such as limited applications.
その他、水、硫酸バンド(化学式:Al2(SO4)3)および、リン酸系重金属固定化剤でアルカリ性の重金属含有灰をリン酸鉛、リン酸カドミウムなどの不溶性の有害金属化合物にして処理する廃棄物処理剤および処理方法が提案されている(特許文献6)
しかし、本発明が無害化処理しようとする対象物は産業廃棄物や都市ごみ(家庭ごみ)などの焼却施設から排出される飛灰(ばいじん)や焼却灰などで硫酸バンドやリン酸系重金属固定剤などの強酸性物質を使用しての水素イオン濃度(pH)の降下は飛灰(ばいじん)中に多量に含まれる未反応消石灰(化学式:Ca(OH)2)などの緩衝作用が強く、硫酸バンドなどの添加量が極端に多くなり、処理後の処理物の成型性が悪くなったり、処理費用が高くなるなどの問題があった。さらに硫酸バンドは吸湿性が高く、固結したり、貯蔵タンク内で腐食が進行するなど課題が多い。
However, the objects to be detoxified by the present invention are fixed to sulfuric acid bands and phosphate heavy metals with fly ash (dust) and incineration ash discharged from incineration facilities such as industrial waste and municipal waste (household waste). The decrease in hydrogen ion concentration (pH) using strong acidic substances such as chemicals has a strong buffering action such as unreacted slaked lime (chemical formula: Ca (OH) 2 ) contained in a large amount in fly ash. There was a problem that the added amount of sulfuric acid band and the like was extremely increased, the moldability of the processed product after processing was deteriorated, and the processing cost was increased. Furthermore, the sulfuric acid band has high hygroscopicity, and has many problems such as solidification and progress of corrosion in the storage tank.
産業廃棄物や都市ごみ(家庭ごみ)などを焼却処理して排出される飛灰(ばいじん)や焼却灰には有害重金属が多く含まれており、何らかの方法で無害化(不溶出化)処理して、埋め立て処分場へ搬出されて処分される。従来は特許文献1〜3に開示されているジエチルジチオカルバミン酸塩など有機液体キレート薬剤が多く用いられて無害化処理されている。 Industrial waste and municipal waste (household waste) are incinerated and fly ash (dust) and incinerated ash contain a lot of toxic heavy metals, which are detoxified (non-eluting) by some method. Then, it is taken out to landfill and disposed of. Conventionally, an organic liquid chelating agent such as diethyldithiocarbamate disclosed in Patent Documents 1 to 3 is often used and detoxified.
これらの有機液体キレート薬剤は人体に有害な臭気成分ガスを発生し、埋立処分後も微生物や菌によって有機物成分が分解され有害金属が再溶出するなどの問題点がある。 These organic liquid chelating agents generate odorous component gases that are harmful to the human body, and there are problems such as decomposition of organic components by microorganisms and fungi and re-elution of toxic metals after landfill disposal.
また、特許文献4〜5などに提案されているアルミニウムシリケートや二酸化ケイ素などの無機粉体状の廃棄物処理剤は固体酸としての中和性能や、吸着剤としての性能が低く、処理材としての添加量が多くなり結果として、処分後の処分量が増量し、埋立処分場の処分寿命を短命化する問題がある。 In addition, waste treatment agents in the form of inorganic powders such as aluminum silicate and silicon dioxide proposed in Patent Documents 4 to 5 have low neutralization performance as solid acids and low performance as adsorbents. As a result, there is a problem that the disposal amount after disposal increases and the disposal life of the landfill site is shortened.
特許文献5に示されているX線的に非晶質な水酸化アルミニウムと粉体状の多孔質無機吸着剤または水溶性リン酸塩と混合物で使用される廃棄物処理剤はアルマイト処理工程で発生する非晶質水酸化アルミニウムを使用することが提案されている。非晶質の水酸化アルミニウムや多孔質の無機吸着剤または水溶性リン酸塩との混合物の廃棄物処理剤は飛灰(ばいじん)中に多く含まれている未反応の水酸化カルシウム(化学式:Ca(OH)2)と反応させて、飛灰からの溶出液中の水素イオン濃度(pH)を降下させて有害重金属を不溶出化させるには多孔質の無機吸着剤や強酸性で緩衝性の強い水溶性のリン酸塩を非晶質の水酸化アルミニウム中に混合しなければならず廃棄物処理剤の製造価格が高くなり、混合材料によっては品質の安定性に欠けるなどの課題がある。 The waste treatment agent used in the mixture of X-ray amorphous aluminum hydroxide and powdered porous inorganic adsorbent or water-soluble phosphate shown in Patent Document 5 is an alumite treatment step. It has been proposed to use the generated amorphous aluminum hydroxide. The waste treatment agent in the mixture of amorphous aluminum hydroxide, porous inorganic adsorbent or water-soluble phosphate is unreacted calcium hydroxide (chemical formula: To react with Ca (OH) 2 ) to lower the hydrogen ion concentration (pH) in the eluate from fly ash and to make toxic heavy metals non-eluting, porous inorganic adsorbents or strong acid buffering A strong water-soluble phosphate must be mixed in amorphous aluminum hydroxide, and the manufacturing cost of the waste treatment agent becomes high, and there are problems such as lack of quality stability depending on the mixed material .
特許文献6に提案されている硫酸バンドやリン酸系重金属固定化剤を用いた廃棄物処理剤は強酸性を示す処理剤で飛灰(ばいじん)と混合混錬する設備などを腐食するなどの課題がある。 Waste treatment agents using sulfate bands and phosphate heavy metal fixing agents proposed in Patent Document 6 are strong acid treatment agents that corrode facilities that mix and knead with fly ash. There are challenges.
本発明は産業廃棄物や都市ごみ(家庭ごみ)などの焼却施設から排出される飛灰(ばいじん)や焼却灰などを人体に有害な臭気ガス成分を発生しないあるいは埋立処分場で処理物が微生物や菌で分解される。あるいは他化合物と混合しない単一化学物質で腐食性の全くない安価な廃棄物処理剤および処理方法を提供することを目的としている。 The present invention does not generate odorous gas components harmful to the human body from fly ash (dust) and incineration ash discharged from incineration facilities such as industrial waste and municipal waste (household waste), or the treated material is microorganisms in a landfill site And decomposed by fungi. Alternatively, an object of the present invention is to provide an inexpensive waste treatment agent and a treatment method which are not mixed with other compounds and are not corrosive at all.
本発明の飛灰(ばいじん)および焼却灰を無害化(不溶出化)処理するため廃棄物処理剤および処理方法は有害な臭気ガス成分などが発生しないあるいは無機化合物混合物の酸性物質で中和反応を主要化学反応ではない無機化合物の単一成分で中性物質である水不溶性塩基性硫酸アルミニウムを用いて、飛灰(ばいじん)や焼却灰を水と共に混合混錬して無害化処理することを特徴とする。
Since the fly ash (industry) and incinerated ash of the present invention are rendered harmless (non-eluting), the waste treatment agent and the treatment method do not generate harmful odor gas components or the like, or neutralize with an acidic substance of an inorganic compound mixture Using water-insoluble basic aluminum sulfate, which is a single component of an inorganic compound that is not a major chemical reaction, and neutral, water ash and incineration ash are mixed and kneaded with water to detoxify it. Features.
本発明ではアルミニウム製品加工工場から排出される硫酸を用いた電解液中の硫酸アルミニウム溶液に水酸化ナトリウム溶液を添加して水素イオン濃度(pH)を4〜8に調整後生成した沈殿を水洗し、脱水、乾燥して製造する水不溶性塩基性硫酸アルミニウムを他の化合物と混合することなく、単一で廃棄物処理材として使用することで課題の解決を図った。 In the present invention, a sodium hydroxide solution is added to an aluminum sulfate solution in an electrolytic solution using sulfuric acid discharged from an aluminum product processing factory to adjust the hydrogen ion concentration (pH) to 4 to 8, and the resulting precipitate is washed with water. The water-insoluble basic aluminum sulfate produced by dehydration and drying was used alone as a waste treatment material without being mixed with other compounds, thereby solving the problem.
本発明の産業廃棄物及び都市ごみ(家庭ごみ)などの焼却施設から排出される飛灰(ばいじん)および焼却灰などを無害化(不溶出化)する廃棄物処理材を水とともに添加し、混合および混錬する処理方法はアルミ製品加工工場の硫酸アルミニウム電解溶液の有効利用の用途が広がり、硫酸アルミニウム廃液を原料にして製造するので他の廃棄物処理剤と比べて極端に安価で商品化が可能で有害な臭気ガスなど発生せずに埋立処分後も微細物や菌に分解されることもなく安定し、環境保全にも大きく寄与する。 Add waste treatment materials that make harmless (non-eluting) waste ash (dust) and incineration ash discharged from incineration facilities such as industrial waste and municipal waste (household waste) of the present invention, and mix The use of aluminum sulfate electrolytic solution in the aluminum product processing plant has expanded the use of aluminum sulfate electrolytic solution, and it is manufactured using aluminum sulfate waste liquid as a raw material, so it can be commercialized at an extremely low price compared to other waste treatment agents. It is stable without being decomposed into fine substances and bacteria after landfill disposal without generating possible harmful odor gas, and greatly contributes to environmental conservation.
以下に実施例や比較例をあげて、本発明を具体的に説明するが本発明はこれに限定されるものではない。本発明の廃棄物処理材の無害化(不溶出化)処理効果や特許文献に例示されている材料との性能を比較するために都市ごみ焼却施設(ガス化溶液炉連続運転)から発生する消石灰(化学式:Ca(OH)2)吹き込み後、バグフィルター式集塵装置で捕集された飛灰(ばいじん)を試験用試料として使用した。飛灰(ばいじん)試料中に含有される有害重金属の中から代表的な項目として鉛(Pb)を選定し、環境庁告示13号法に記載されている溶出試験方法により、検液を作成して、原子吸光光度計により、分析試験を行い、陸上埋立基準値(Pb=0.3mg/l)を用いて各種の試験評価を求めた。 Hereinafter, the present invention will be specifically described with reference to examples and comparative examples, but the present invention is not limited thereto. Slaked lime generated from municipal waste incineration facility (continuous operation of gasification solution furnace) to compare the detoxification (non-eluting) treatment effect of the waste treatment material of the present invention and the performance of materials exemplified in the patent literature (Chemical formula: Ca (OH) 2 ) After blowing, fly ash (dust) collected by a bag filter type dust collector was used as a test sample. Select lead (Pb) as a representative item from the toxic heavy metals contained in fly ash samples, and prepare a test solution by the dissolution test method described in the Environmental Agency Notification No.13 Then, an analytical test was performed with an atomic absorption photometer, and various test evaluations were obtained using the landfill reference value (Pb = 0.3 mg / l).
アルミニウム製品加工工場のアルマイト表面処理工程で使用される硫酸の電解溶液から排出される硫酸アルミニウム廃液を使用して硫酸アルミニウム廃液中(pHは約2.8)に水酸化ナトリウム水溶液(20重量パーセント)を、添加して、水素イオン濃度(pH)を4.0〜13.0の範囲に調整して沈殿物を生成させて回収し、水洗浄後に乾燥し、本発明の廃棄物処理材である水不溶性塩基性硫酸アルミニウム粉末をpHを4から8に調整して製造したものを処理材4から8の5条件に分別して表示し、pHを9から13に調整して製造した粉末試料を比較例1から5の5条件で表1に示した。乾燥して廃棄物処理剤の水不溶性塩基性硫酸アルミニウムを製造して廃棄物処理剤としての性能評価を表1に示す。 Using an aluminum sulfate waste solution discharged from an electrolytic solution of sulfuric acid used in an alumite surface treatment process of an aluminum product processing factory, an aqueous solution of sodium hydroxide (20 weight percent) in the aluminum sulfate waste solution (pH is about 2.8), Add, adjust the hydrogen ion concentration (pH) to the range of 4.0 to 13.0 to produce a precipitate, collect it, dry it after washing with water, and use it as a waste treatment material of the present invention. Powders prepared by adjusting the pH from 4 to 8 are classified and displayed in 5 conditions of treatment materials 4 to 8, and powder samples manufactured by adjusting the pH from 9 to 13 are shown in 5 of Comparative Examples 1 to 5. The conditions are shown in Table 1. Table 1 shows the performance evaluation as a waste treatment agent by producing water-insoluble basic aluminum sulfate as a waste treatment agent after drying.
性能評価試験は飛灰(ばいじん)試料に水素イオン濃度を調整した。 In the performance evaluation test, the hydrogen ion concentration was adjusted to the fly ash sample.
廃棄物処理材を飛灰試料に対して重量比で各々8および10パーセント添加し、同様にして各々水40重量パーセント添加して混合混錬して性能評価用供試料とした。 The waste treatment material was added at 8 and 10 percent by weight with respect to the fly ash sample, respectively, and similarly 40 percent by weight of water was added and mixed and kneaded to obtain a sample for performance evaluation.
表1から明らかなように硫酸アルミニウム廃液から水不溶性塩基性硫酸アルミニウム廃棄物処理材を製造する場合のpH調整範囲は4〜8が適切であり、8を超えるとX線的には非晶質であっても限りなく水酸化アルミニウム(化学式:Al(OH)3)が多くなり、硫酸基(化学式SO4)の含有量が極端に少なくなり、鉛(Pb)の不溶出化性能が低下する。 As is apparent from Table 1, the pH adjustment range for producing a water-insoluble basic aluminum sulfate waste treatment material from an aluminum sulfate waste liquid is suitably 4 to 8, and if it exceeds 8, it is amorphous in X-rays However, the amount of aluminum hydroxide (chemical formula: Al (OH) 3 ) increases as much as possible, the content of sulfate groups (chemical formula SO 4 ) becomes extremely small, and the performance of non-eluting lead (Pb) decreases. .
本発明でアルマイト表面処理工程から排出される硫酸アルミニウム廃液から水酸化ナトリウム添加による水不溶性塩基性硫酸アルミニウム廃棄物処理材の製造時の水素イオン濃度(pH)調整範囲は4〜8が適切であるが望ましくはpH=6〜8の範囲で製造された廃棄物処理材が最も望ましい。
In the present invention, the hydrogen ion concentration (pH) adjustment range in the production of the water-insoluble basic aluminum sulfate waste treatment material by adding sodium hydroxide from the aluminum sulfate waste solution discharged from the anodized surface treatment step is suitably 4-8. However, it is most desirable to use a waste treatment material manufactured in the range of pH = 6-8.
本発明の廃棄物処理材の性能評価するために実際のアルミニウム製品加工工場のアルマイト処理工程から排出される硫酸アルミニウム電解廃液を再利用するために加工された製品や、多孔質の無機粉体吸着剤あるいは廃棄物処理材の原材料として提案されている。無機化合物などを比較例として無害化(不溶出化)処理効果の試験を行った。 In order to evaluate the performance of the waste treatment material of the present invention, the product processed to recycle the aluminum sulfate electrolysis waste liquid discharged from the alumite treatment process of the actual aluminum product processing factory, and the porous inorganic powder adsorption It has been proposed as a raw material for chemicals or waste treatment materials. A test for detoxification (non-eluting) treatment effect was conducted using an inorganic compound as a comparative example.
試験は無害化処理効果を確認するために実施例1に用いた飛灰(ばいじん)試料に対して本発明の廃棄物処理材およびそのほかの処理材あるいは処理材原料の試薬などを重量比によって各8,10,12,14%添加し、混合混錬後環境庁告示第13号法による溶出試験を行い、原子吸光光度法により鉛(Pb)の測定を行った。 In the test, the waste treatment material of the present invention and other treatment materials or treatment material raw materials were each measured by weight ratio with respect to the fly ash sample used in Example 1 to confirm the detoxification treatment effect. 8, 10, 12, 14% was added, and after mixing and kneading, an elution test was conducted by the Environmental Agency Notification No. 13 method, and lead (Pb) was measured by atomic absorption spectrophotometry.
試験に供した処理材および原材料の詳細を表2に示す。 Table 2 shows the details of the treated materials and raw materials used in the test.
表2に記載した本発明の廃棄物処理材および他材料などの無害化(不溶出化)処理効果についての試験結果を表3に示す。 Table 3 shows the test results on the detoxification (non-eluting) treatment effect of the waste treatment material and other materials of the present invention described in Table 2.
表3に見られるように本発明の廃棄物処理材である水不溶性塩基性硫酸アルミニウムおよび化合形態が同じで市販品のアルミナホワイトなどが効果的に作用していることが確認できる。その他、市販の硫酸アルミニウムも無害化作用が認められるが、貯蔵タンク内での吸湿性や強酸性による設備の腐食などが問題となり、商品化は難しい。 As seen in Table 3, it can be confirmed that the water-insoluble basic aluminum sulfate, which is the waste treatment material of the present invention, and the compound form are the same, and commercially available alumina white or the like acts effectively. In addition, although commercially available aluminum sulfate is also recognized as detoxifying, it is difficult to commercialize due to problems such as hygroscopicity in the storage tank and corrosion of equipment due to strong acidity.
表3の中で無害化処理の効果が確認できた材料や化合物はいずれも硫酸(SO4)基を含有しており、本発明の廃棄物処理材の中での重要な役割を、果たしているので欠かすことができない事が明らかである。
In Table 3, the materials and compounds for which the effect of detoxification treatment could be confirmed all contain sulfuric acid (SO 4 ) groups and play an important role in the waste treatment material of the present invention. It is clear that it is indispensable.
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