WO1980001249A1 - Solidification of harmful solid waste - Google Patents

Solidification of harmful solid waste Download PDF

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Publication number
WO1980001249A1
WO1980001249A1 PCT/JP1978/000062 JP7800062W WO8001249A1 WO 1980001249 A1 WO1980001249 A1 WO 1980001249A1 JP 7800062 W JP7800062 W JP 7800062W WO 8001249 A1 WO8001249 A1 WO 8001249A1
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WO
WIPO (PCT)
Prior art keywords
cement
lipid
amount
oil
solidified
Prior art date
Application number
PCT/JP1978/000062
Other languages
French (fr)
Japanese (ja)
Inventor
H Kubota
Original Assignee
Taken Aka Komuten Kk
H Kubota
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Taken Aka Komuten Kk, H Kubota filed Critical Taken Aka Komuten Kk
Priority to PCT/JP1978/000062 priority Critical patent/WO1980001249A1/en
Publication of WO1980001249A1 publication Critical patent/WO1980001249A1/en

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Classifications

    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/04Waste materials; Refuse
    • C04B18/0463Hazardous waste
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B28/00Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
    • C04B28/02Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing hydraulic cements other than calcium sulfates
    • GPHYSICS
    • G21NUCLEAR PHYSICS; NUCLEAR ENGINEERING
    • G21FPROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
    • G21F9/00Treating radioactively contaminated material; Decontamination arrangements therefor
    • G21F9/28Treating solids
    • G21F9/30Processing
    • G21F9/301Processing by fixation in stable solid media
    • G21F9/302Processing by fixation in stable solid media in an inorganic matrix
    • G21F9/304Cement or cement-like matrix
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/00474Uses not provided for elsewhere in C04B2111/00
    • C04B2111/00767Uses not provided for elsewhere in C04B2111/00 for waste stabilisation purposes
    • C04B2111/00784Uses not provided for elsewhere in C04B2111/00 for waste stabilisation purposes for disposal only
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

Definitions

  • the present invention provides a mud, powder or granular material that, if left unchecked, is contaminated with toxic substances that may directly or indirectly adversely affect ecosystems.
  • Hazardous wastes such as various industrial wastes and sedimentary mud or soil (hereinafter referred to simply as "hazardous wastes" in the present invention) are referred to as landfill embankment, embankment,
  • the hazardous waste is solidified in order to recycle it as a useful material for molded materials, such as D used for reclamation and land development.
  • the technology relates to a technique for trapping harmful pollutants contained in a substance in a solidified substance and detoxifying the substance, such as the generation of secondary pollution.
  • hazardous waste such as sludge that accumulates as sediment of nearby rivers, ports, lakes and marshes, and sludge discharged from the chemical industry or various industries that use chemicals
  • inorganic harmful pollutants such as heavy metals
  • many cases contain organic chlorine compounds, phosphorus compounds, sulfur compounds, nitrogen compounds, arsenic compounds, mercury compounds, copper compounds, and the like. If left unchecked, it will cause various harmful effects on the ecosystem and cause serious environmental problems as a source of environmental pollution.Therefore, urgent measures are needed in this area.
  • As a measure for detoxifying such hazardous wastes a common method that has been practiced in the past is to use conventionally known hydraulic cement or water for hazardous wastes.
  • the object of the present invention is to effectively fix even organic harmful contaminants which have been difficult to fix by using the cement solidifying material alone as described above, and We do not propose a method that can be implemented very easily, both practically and economically.
  • the lipid is selected in consideration of its acid value, iodine value, oxidation value, melting point (or freezing point), refractive index, carbon number, and compatibility with organic harmful substances. It is necessary, but practically, most fatty oils or fatty acids that are liquid at room temperature are useful.
  • the amount of lipid added depends on the type and content of hazardous pollutants in hazardous waste, the type and state of lipids used, and the amount of hazardous pollutants from solidified matter. Forgiveness
  • lipid dispersion treatment is performed by blending with the cement-based hardening material, the interaction with the oil-based hardening material during a long period To avoid reaction, use fatty acids or fatty oils with particularly high acid value as the quality of use. That is not good.
  • Hazardous torment substances containing organic harmful pollutants solidified by this method have the property that the organic harmful pollutants contained in the substance themselves inhibit the growth of microorganisms. Therefore, despite the fact that the lipid is relatively biodegradable when added and mixed, the effect of fixing the organic harmful contaminants in the listening period is maintained for a long period of time. Paradoxically, it can be said that as long as the organic harmful contaminants are present in the solidified substance, its fixing effect is not lost, but In addition, lipids eventually react with calcium hydroxide, which is a hydration product of cement-based solidifying materials, to be able to resist biodegradability and to be chemically The conversion to highly stable hydrophobic calcium limestone also contributes to the long-lasting effect of fixing organic harmful pollutants.
  • calcium hydroxide which is a hydration product of cement-based solidifying materials
  • the added lipid reacts with heavy metals contained in the hazardous waste to form heavy metal stones which are insoluble in water and have a bactericidal or fungicidal effect.
  • heavy metals contained in the hazardous waste to form heavy metal stones which are insoluble in water and have a bactericidal or fungicidal effect.
  • Formed and, in the presence of cement-based solidifying material, has the effect of confining and fixing the hydrated product in a matrix; also has the effect of fixing various heavy metals and organic harmful substances. It is extremely effective as a method for solidifying hazardous waste products that also contain substances.
  • the hydraulic cement used as the cement-based solidifying material the following can be used: Baltland cement (ordinary, early strength, and c-vpi).
  • Various portland cements, such as super-high strength, are desirable in terms of effectiveness and economy, but blast furnace cement, silica cement, flyer It is acceptable to use slush cement, bozolan cement, or high-aluminum cement.
  • the present inventor has obtained further new findings as described below while continuing the experimental cutting of the above method.
  • the existing hydraulic cement is not used alone as the cement-based solidifying material, but these hydraulic cements are used.
  • the use of cement-based solidified cement containing the following additives with the main composition X.II), solidification of hazardous waste and removal of hazardous pollutants in hazardous waste materials It has been found that the containment effect is dramatically increased.
  • the cement-based solidifying material is composed of [ ⁇ ] hydraulic cement, [B] aluminum sulfate, bright ban, ferrous sulfate, and ferrous sulfate. At least one sulfate selected from the group consisting of:
  • the fats and oils react with the hydrated product (calcium hydroxide) of the cement-based solidifying agent to be degraded, thereby exhibiting the effect of continuously fixing organic harmful pollutants.
  • the alkaline earth metal hydroxide required for the above-mentioned deterioration is generated from cement solidified material. Since it must be provided only from the hydrated product, its oxidation reaction proceeds slowly and in a limited amount of time and quantitatively, waiting for the production of the hydrated product. This will be.
  • the cement solidifying material is used in combination with a sufficient amount of alkaline metal hydroxide (from the above-mentioned component [D ),
  • the oils and fats can be rapidly and completely removed without waiting for the raw K of the hydrated K material of the cement solidified material. I suppose that the excellent effects as described above can be obtained.
  • the amount of each component to be used in the cement-based solidifying material containing the additive is usually determined according to the following general rule.
  • Principle 3 The ratio of the total amount of the components [:], [: C] and [D] to the hydraulic cement [A] is almost 0 ⁇ 05 in terms of anhydride. Must be within the range of 1.
  • the optimal amount of each component in the solidified material), [B], [C], and [D] can be determined. Type, water content in hazardous waste materials, harmful pollutants and hydraulics contaminated in waste materials, hydration of hydraulic cement, content of interfering substances, already mixed from the beginning The content of the same kind of components as [B], [C], and [D], and the performance expected of the finally obtained solidified product, etc., may be appropriately modified. You can do it.
  • the hazardous waste is sewage sludge dewatering cake, etc.
  • a large amount of lime as a super-aid is mixed, so that the component [D] may be used in a considerable amount. Can be deducted.
  • the hazardous waste is metal pickling sludge, flue gas desulfurization sludge, etc.
  • lime used as a neutralizing agent was included too much j?
  • the ratio of each component in the additive is appropriately determined in consideration of the amount and chemical properties of these substances.
  • the present invention provides a cement-based solidifying material (most preferred).
  • This is a very simple method of adding a small amount of fat to the above-mentioned additive-incorporated [5 cement-based solidifying material], and is practically and economically. It is extremely easy to implement.] 3
  • organic harmful substances which were difficult to fix by the conventional method described above, can be securely contained and fixed. It has a remarkable advantage of being able to maintain a long-lasting, excellent containment and fixing effect that does not cause secondary pollution due to elution.
  • the industrial profits that contribute to the economy are enormous.
  • cement-based solidifying material used in the present invention the above-described iP cement-based solidifying material containing an additive aid is most preferred.
  • this is not a limitation, and as described in the first part of this chapter, as long as hydraulic cement is used as the main material, existing cement-based cement Is not always applicable.
  • a water reducing agent, a setting accelerator, and a setting retarder used as a normal cement admixture or as an admixture with respect to the cement solidification agent used in the present invention.
  • Agents, foaming agents, foaming agents, water-proofing agents, coloring agents, fungicides, antibacterial agents, fibrous reinforcing materials, fillers, polymeric admixtures, pozzolanic admixtures, a On sealants, surfactants, intumescents, etc. can be used in combination depending on the purpose of each, as long as there is no particular problem.
  • dredged sludge from harbor sediment and river sediment containing various harmful pollutants moisture content and harmful pollutant content of each dredged sludge are shown in Table 1, the latter In the case of river sediment dredging, the appropriate amount of parathion and methylmercury is added to artificially further contaminate the riverbed).
  • the material was solidified with the existing cement-based solidified material, and the unconfined compressive strength of each solid and the amount of harmful pollutants eluted were examined.
  • the solidification method is as follows: 100 parts of dredged sludge (hereinafter, “part” means all parts by weight) in the present specification. First, 0.3 parts of lipid was added and mixed, and then, 20 parts of cement solidified material was added and mixed.
  • Example 11 From the results of Example 11, it is found that when a small amount of cement is used in combination with various cement-based solidifying materials, the uniaxial compressive strength of the solidified product is slightly reduced, but the effect of harmful pollutants is significantly reduced. You can see that it improves. 9) In other words, the effect of using a cement-based solidifying material with additive and lipid in combination is remarkable.
  • Suspension A small amount of a nonionic surfactant is added to a composition of net lipid 20 and bentonite 20% water 60, and the mixture is stirred and mixed. What I did
  • Blemix Cement-based solidifying material with soybean oil at a specified concentration
  • the type of lipid, its state, and the order of addition are as follows: It has little effect on the fixation effect of CB, but it was found that the effect decreased when the amount of lipid added was reduced below a certain limit. However, it can be said that practically even if the amount of lipid added is extremely small, it is effective.
  • the present invention is not limited to heavy metals in hazardous wastes, but can be fixed by the conventional cement-based solidifying material alone. Organic harmful contaminants, which had been difficult, can be contained and fixed to the extent that there is no need to worry about the occurrence of secondary pollution due to re-elution. Also, in the present invention, the lipids newly added to be used in combination are relatively easily available: 3 ⁇ 4 Many are available, and therefore, both practical and economical are extremely easy. And its industrial benefits are enormous;

Abstract

Harmful solid waste containing harmful pollutants such as heavy metals, harmful organic pollutants and the like is added and mixed with lipids and cement-based solidifying agent consisting essentially of hydraulic cement to be solidified, thereby effectively preventing the elution of the harmful pollutants.

Description

α )  α)
明 細. 書  Specification
有害廃棄物の固化方法  How to solidify hazardous waste
技 術 分 野  Technical field
本発明は、 放置 したま ま に し てお く と 、 直接的ま たは 間接的に生態系 に有害作用 を及ぼすおそれがあ る毒性物 質で汚染さ れた泥状、 粉状或いは粒状の各種産業廃棄物 や水底堆積泥土若 し く は土壌 な どの有害廃棄物 ( 以下、 本発明においては 、 これ ら を総称 して単に有害廃棄物 と 言 う ) を 、 例えば、 埋立て盛土、 築堤、 干拓、 土地造成 等の土木材料に供 した D 、 何 ら かの有用 な 成型物の素材 と し て再生利用す る な どのため に 、 当該有害廃棄物 を固 化する と 同時に 、 こ の有害廃棄物中 に含有されて い る有 害汚染物質を 固化物中 に封 じ込め て 、 二次公害の発生な ど力; い よ う に無害化処理する技術 関する 。  The present invention provides a mud, powder or granular material that, if left unchecked, is contaminated with toxic substances that may directly or indirectly adversely affect ecosystems. Hazardous wastes such as various industrial wastes and sedimentary mud or soil (hereinafter referred to simply as "hazardous wastes" in the present invention) are referred to as landfill embankment, embankment, At the same time as solidifying the hazardous waste, the hazardous waste is solidified in order to recycle it as a useful material for molded materials, such as D used for reclamation and land development. The technology relates to a technique for trapping harmful pollutants contained in a substance in a solidified substance and detoxifying the substance, such as the generation of secondary pollution.
冃 京 技 術  京 Kyoto Technology
一般に、 工業地帯 近隣する河川、 港湾、 湖沼等の底 質 と し て堆積す る 汚泥や、 化学工業若 し く は化学薬品 を 使用する諸工業か ら 排出される ス ラ ッ ジ等の有害廃棄物 に は、 重金属類等の無機性有害汚染物質のほかに 、 有機 性の塩素化合物、 燐化合物、 硫黄化合物、 窒素化合物、 砒素化合物、 水銀化合物、 銅化合物 る どを含有する ケ - ス が多 く 、 これを放置 し てお く と 生態系に種々 の有害作 用 を及ぼ し、 環境公害源 と し て深刻 ¾社会問題を 惹起す る ので、 こ の面での対策の急務が要望されてい る 。 . こ の よ う な有害廃棄物の無害化処理対策と して、 従来 から実施されて い る一般的 方法 と し て、 有害廃棄物に 従来公知の水硬性セ メ ン ト 若 し く は水硬性を有する セ メ ン ト 質 ぐ 石膏質を も 含む ) を主成分 と するセ メ ン ト 系固 ィヒ材を添加混合 して固化する こ と に よ !) 、 その固化物中 に有害汚染物質を封 じ込める方法があ る力;、 この よ う な 既存のセ メ ン ト 系固化材の単独使用に よ る固化処理方法 では、 重金属類等を封 じ込め固定する こ とはでき て も 、 有機性の有害汚染物質に対 しては、 そ の有効性に疑問が あ ]? 、 場合に よっては、 却って固化物から の有機性有害 汚染物質の再溶出に よ る二次公害を助長するが如き逆効 果を も た らすこ と も あった。 In general, hazardous waste such as sludge that accumulates as sediment of nearby rivers, ports, lakes and marshes, and sludge discharged from the chemical industry or various industries that use chemicals In many cases, in addition to inorganic harmful pollutants such as heavy metals, many cases contain organic chlorine compounds, phosphorus compounds, sulfur compounds, nitrogen compounds, arsenic compounds, mercury compounds, copper compounds, and the like. If left unchecked, it will cause various harmful effects on the ecosystem and cause serious environmental problems as a source of environmental pollution.Therefore, urgent measures are needed in this area. . As a measure for detoxifying such hazardous wastes, a common method that has been practiced in the past is to use conventionally known hydraulic cement or water for hazardous wastes. (Including cementitious gypsum, which is hard), and solidify by adding and mixing cementitious stiffeners whose main component is! ), The ability to contain harmful pollutants in the solidified product; the solidification method using only the existing cement-based solidifying material alone does not remove heavy metals, etc. Even if it can be fixed, the effectiveness of organic harmful pollutants is questionable.]? In some cases, organic harmful pollutants from solidified substances In some cases, re-elution promoted secondary pollution, but had the opposite effect.
かかる傾向の原因は、 前述の ご と き有機性の有害汚染物 質の多 く 力;、 本質的にセ メ ン ト 系固化材の水和生成物と の化学的若 し 〈 は物理的親和性に乏 しいこ と に よ る も の であるが、 場合.に よ っては、 セ メ ン ト 系固化材の水和過 程 おける ア ル カ リ メ ディ アム の生成に よ ]? 、 有機性有 害汚染物質の水に対する溶解度が増大する こ と 起因す る こ と も あ る。 The cause of this tendency is that many of the organic harmful pollutants mentioned above; the chemical compatibility with the hydration products of the cement solidified material essentially < This is due to the lack of properties, but in some cases, due to the formation of an alkaline medium during the hydration process of the cement cement.]? It may also be due to increased solubility of organic harmful pollutants in water.
発 明 の 開 示  Disclosure of the invention
本発明の 目的は、 特に、 既述の よ う なセ メ ン ト 系固化 材の単独使用では固定困難であった有機性の有害汚染物 質を も効果的 固定する こ とができ 、 かつ、 実用的に も ま た経済的に も極めて容易に実施 し得る方法を提案せん  In particular, the object of the present invention is to effectively fix even organic harmful contaminants which have been difficult to fix by using the cement solidifying material alone as described above, and We do not propose a method that can be implemented very easily, both practically and economically.
.'.PI. '. PI
- 0 ノ と する 点に あ る 。 - 本発明者は 、 重金属類等の有害汚染物質のほかに種 々 の有機合成農薬類や、 P CB 、 ア ル キ ル水銀等の有機性有 害汚染物質を含有す る各種有害廃棄物を 、 既存の各種セ メ ン ト 系固化材を 用いて固化 し、 そ の 固化物中に有害汚 染物質を封 じ込め固定する方法の研究を推進 し て行 く う ち に、 前記セ メ ン ト 系固化材に少量の脂肪油ま たは脂肪 酸、 或いは両者の混合物、 若 し く は それ ら を主成分 と す る脂質 ( 以下、 本明細書において は 、 総称 して単に脂質 と 記載する 。 ) を併用する と い う 新規な方法に よ !) 重金 属類は も と よ ]) 、 特に有機性の有害汚染物質を極めて効 杲的 固化物中 に封 じ込め固定で き 、 それら の再溶出 を 防止 し得る こ と を知見する に至った。 即 ち、 多 く の有 機性有害汚染物質は、 セ メ ン ト 系固化材の水和生成物 と の親和性 乏 しいために 、 その 固定が困難であ るが、 こ れ ら 有機性有害汚染物質と の親和性に富む脂質を介すれ ば、 セ メ ン ト 系固ィヒ材の水和生成物の マ ト リ ッ ク ス 中 に それ ら を 極め て効果的に封 じ込め得る こ と を実験に よ つ て知見得 したの で あ る 。 -0 no The point is that. -The present inventor considers various organic wastes containing various synthetic organic pesticides and organic toxic contaminants such as PCB and alkylmercury in addition to harmful contaminants such as heavy metals. In the course of promoting research on a method of solidifying using various existing cement-based solidifying materials and encapsulating and fixing harmful pollutants in the solidified material, the aforementioned cement was developed. A small amount of fatty oil or fatty acid, or a mixture of both, or a lipid containing both as a main component (hereinafter referred to simply as a lipid in the present specification) )) A new method of using together! ) Despite the heavy metals, it has been found that particularly harmful organic contaminants can be contained and fixed in an extremely effective solidified substance, and that they can be prevented from re-eluting. . Immediately, many organic harmful pollutants are difficult to fix due to poor affinity with the hydrated products of cement-based solidifying materials. Through lipids, which have a high affinity for contaminants, they can be extremely effectively contained in the matrix of hydrated products of cement-based hardwood. And were obtained through experiments.
一般的に、 有機性有害汚染物質の 多 く の も のは、 そ の も の 自 体が親油性に富む も のであ る ため、 脂質に溶解 し た 、 吸着 した 、 脂質 と 溶媒和 を形成 した !) 、 ^いは 脂質の不飽和結合部に付加 して脂質に 固定さ れる性質を 有す る も ので あ るが、 かかる 状態 に形成.された脂質は 、 更にセ メ ン ト 系固化材の水和生成物であ る水酸化カ ル シ ゥ ム と結合 して、 一層安定な、 かつ疎水性に富む力 ル シ ゥ ム石鹼に転化 し、 それ 自体が有機性有害汚染物質の担 体 と なって、 セ メ ン ト 系固化材の水和生成物のマ ト リ ッ ク ス 中 封 じ込め られる ので、 後述する如き本発明の卓 効が得られる も の と考えられる。 In general, many of the organic toxic pollutants formed solvates with, dissolved, and adsorbed to lipids because they were themselves lipophilic. ! ), Which has the property of being added to the unsaturated bond of lipid and fixed to the lipid, but the lipid formed in such a state is Furthermore, it combines with calcium hydroxide, which is a hydration product of cement-based solidification material, to convert it into more stable and highly hydrophobic rubystone. Serves as a carrier for organic harmful pollutants and is contained in the matrix of the hydrated product of the cement-based solidifying material, so that the effects of the present invention described below can be obtained. It is considered to be something.
前記脂質と し ては、 そ の酸価、 沃素価、 鹼化価、 融点 ( ま たは凝固点 ) 、 屈折率、 炭素数、 有機性有害物質と の相溶性: ¾ どを考慮 し て選択する必要があるが、 実用的 には、 常温で液状を なす脂肪油若 し く は脂肪酸であれば 大部分の も のは有用である。  The lipid is selected in consideration of its acid value, iodine value, oxidation value, melting point (or freezing point), refractive index, carbon number, and compatibility with organic harmful substances. It is necessary, but practically, most fatty oils or fatty acids that are liquid at room temperature are useful.
然し乍ら、 経済的見地からすれば、 上記方法を実施す るために特別に精製 した高価る も のを用いる よ も 、 粗 製品若 し く は廃食用油、 ま たは各種油剤製造若 し く は油 脂精製過程で副生される脂肪油や脂肪酸を含む副産物若 し く は廃棄物を使用するのが好ま し く 、 特に多量の脂質 を吸着 した油脂精製廃白土は有用で あ る 。 殊に こ の場 合には、 付加価値の乏 しい副産物や廃棄物の処理を兼ね て、 これらを有効に再利用する こ と ができ る と いった極 め て大き な副次的効果があっ て 、 本方法を実施する上で の意義は一層大き い。  However, from an economic point of view, rather than using specially refined and expensive ones to carry out the above process, crude or waste edible oils or various oil preparations must be used. It is preferable to use by-products or waste products containing fatty oils and fatty acids produced as a by-product in the oil and fat refining process, and particularly, fat and oil refining waste clay adsorbing a large amount of lipids is useful. In this case, in particular, there is an extremely large side effect that the waste can be effectively reused while also treating the by-products and wastes with low added value. Therefore, the significance of implementing this method is even greater.
本方法の実施に あたって、 脂質の添加量は、 有害廃棄 物中の有害汚染物質の種類と そ の含有量、 使用する脂質 の種類お よびそ の状態、 固化物か らの有害汚染物質の許  In carrying out this method, the amount of lipid added depends on the type and content of hazardous pollutants in hazardous waste, the type and state of lipids used, and the amount of hazardous pollutants from solidified matter. Forgiveness
00
—0 ; 容溶出量 な どを考慮 し て決定すべ き であ る が、 一般的に は、 脂質の添加量に比例 して有害汚染物質の 固定効果は 向上 し、 あ る一定限度に達する と 頭打ち と ]? 、 不必要 に 多量に添加す る と 、 む し ろ固化物の 固化強度を低下さ せるため好ま し く い。 通常は 、 対象 と ¾ る有害廃棄 物中の有害汚染物質の含有量が極め て微量であ るため、 脂質の添加量 も ま た、 これに応 じて微量で充分であ 、 例えば、 水底堆積物 と しての汚染底質の浚渫汚泥の ご と き 場合では、 汚泥重量の約 10 . 000 分の 1 い し 2 0 分 の 1 程度の範囲の少量で充分で あ る —0 ; It should be determined by taking into account the dissolution amount, etc., but in general, the effect of fixing harmful pollutants improves in proportion to the amount of lipid added, and reaches a certain limit and peaks off.] However, it is not preferable to add an unnecessarily large amount, since the solidification strength of the solidified product is rather lowered. Normally, the amount of harmful pollutants in the target hazardous waste is extremely small, so that the amount of lipid added should be correspondingly small and sufficient. In the case of dredged sludge with contaminated sediment as a material, a small amount in the range of about 1 / 10,000 to 1/20 of the sludge weight is sufficient.
しカゝ し て 、 かか る 少量の脂質を 多量の有害廃棄物 加混合 して十分に分散させるため に 、 添加すべき 予め界面活性剤等を 用いてェ マ ル ジ ヨ ン ィ匕 した  Then, in order to sufficiently disperse such a small amount of lipid by adding a large amount of hazardous waste, emulsification was carried out in advance using a surfactant or the like to be added.
をベ ン ト ナイ ト な どの水中懸濁液中 に分散させ (: 性剤を併用 して も よ い ) て使用 した 、 或いは、 量の脂質を予めセ メ ン ト 系固化材に均等に混和 し レ ミ ッ タ スの状態で使用する こ と に よ って も 可能 ま た、 脂質 と セ メ ン ト 系固化材を 有害廃菜物中へ る順序は 、 同時であ って も 、 別 々 .で あって も 、 い 先行 し て も 、 特に こ だわる も のでは ない 。 し力 し セ メ ン ト 系固ィヒ材 と の ブ レ ミ ッ ク ス化に よ る脂質 分散処理を施す場合には、 聍葳期間中 におけ る脂 メ ン ト 系固化材 と の相互反応を避け るため 、 使用 質 と し て は、 脂肪酸や特に酸価の 高い脂肪油を使 こ とは.好ま し く ない。 Was dispersed in a suspension in water such as bentonite (or may be used in combination with a sexual agent), or the amount of lipid was previously mixed evenly with the cement solidified material. It is also possible to use lipids and cement-based solidifying materials in hazardous waste vegetables, even if they are used in a state of remittance. It doesn't matter what you do, even if you're ahead of it. When the lipid dispersion treatment is performed by blending with the cement-based hardening material, the interaction with the oil-based hardening material during a long period To avoid reaction, use fatty acids or fatty oils with particularly high acid value as the quality of use. That is not good.
本方法に よつ'て固化処理 された有機性有害汚染物質を 含有する有害虎秦物は、 そ の も の自体に含有 されて い る 有機性有害汚染物質が微生物の増殖作用を阻止する性質 を有するため、 添加混合 し 7 脂質が比較的生分解性を有 する も のであるに も拘わらず長期に亘つて有機性有害污 染物質の ,听期固定効果を持続する。 こ れを逆説的に言 えば、 固化物中に有機性有害汚染物質が存在する限 、 その固定効果は失るわれな いこ と を意味する も のと言 う こ とがで き るが、 更にま た、 脂質は最終的にはセ メ ン ト 系固化材の水和生成物であ る水酸化 カ ル シク ム と反応 し て、 よ 生分解性に抗 し得て、 かつ化学的に も安定性の 良い疎水性のカ ル シ ク ム石鹼に転化する ため、 こ の点カ ら も有機性有害汚染物質の固定効果の長期持続性が助長 さ れ る 。  Hazardous torment substances containing organic harmful pollutants solidified by this method have the property that the organic harmful pollutants contained in the substance themselves inhibit the growth of microorganisms. Therefore, despite the fact that the lipid is relatively biodegradable when added and mixed, the effect of fixing the organic harmful contaminants in the listening period is maintained for a long period of time. Paradoxically, it can be said that as long as the organic harmful contaminants are present in the solidified substance, its fixing effect is not lost, but In addition, lipids eventually react with calcium hydroxide, which is a hydration product of cement-based solidifying materials, to be able to resist biodegradability and to be chemically The conversion to highly stable hydrophobic calcium limestone also contributes to the long-lasting effect of fixing organic harmful pollutants.
ま た、 本方法に よれば、 添加 した脂質が有害廃棄物中 に含有 されている重金属類 と も反応 して、 水に不溶性で かつ防菌 も し く は防かび効果を有する重金属石鹼を形成 し、 セ メ ン ト系固化材 と の共存下で、 その水和生成物の マ ト リ; ッ ク ス中に封 じ込め固定する効果を も有 し、 各種 重金属類お よび有機性有害物質を併せ含有する有害廃秦 物の固化方法 と して甚だ有効であ る。  Further, according to the present method, the added lipid reacts with heavy metals contained in the hazardous waste to form heavy metal stones which are insoluble in water and have a bactericidal or fungicidal effect. Formed and, in the presence of cement-based solidifying material, has the effect of confining and fixing the hydrated product in a matrix; also has the effect of fixing various heavy metals and organic harmful substances. It is extremely effective as a method for solidifying hazardous waste products that also contain substances.
なお、 前記セ メ ン ト系固化材 と して用 い られる水硬性 セ メ ン ト と しては、 ボ ル ト ラ ン ド セ メ ン ト ( 普通、 早強、 ひ c-vpi 超早強等 の各種ポ ル ト ラ ン ドセ メ ン ト を含む ) が効果お よ び経済性において望ま し いが、 高炉 セ メ ン ト 、 シ リ カ セ メ ン ト 、 フ ラ イ ァ ッ シ ュ セ メ ン ト、 ボ ゾ ラ ン セ メ ン ト 高 ァノレ ミ ナ質 セ メ ン ト等を使用 し て も差支え な い。 As the hydraulic cement used as the cement-based solidifying material, the following can be used: Baltland cement (ordinary, early strength, and c-vpi). Various portland cements, such as super-high strength, are desirable in terms of effectiveness and economy, but blast furnace cement, silica cement, flyer It is acceptable to use slush cement, bozolan cement, or high-aluminum cement.
更 に加えて、 本発明者は、 上記方法に関す る実験的斫 究を継続す る う ち に 、 以下 の如 き 更に新 し い知見を得る に至つた。 即 ち 、 目 U sfi し た方法 におい て、 セ メ ン ト 系 固化材 と し て既存の水硬性セ メ ン ト を単独 に用 い るので は な く 、 これ ら の水硬性 セ メ ン ト を主材 に し た下記の如 き 構成の添加助剤入 セ メ ン ト系固化材を用 い る こ と に X. Ϊ) 、 有害廃棄物の固化及び有害廃棄物質中 の有害汚染 物質の封 じ込め固定効果が飛躍的に属増大す る こ と が判 明 した の であ る。  In addition, the present inventor has obtained further new findings as described below while continuing the experimental cutting of the above method. In other words, according to the method used in the present invention, the existing hydraulic cement is not used alone as the cement-based solidifying material, but these hydraulic cements are used. The use of cement-based solidified cement containing the following additives with the main composition X.II), solidification of hazardous waste and removal of hazardous pollutants in hazardous waste materials It has been found that the containment effect is dramatically increased.
こ の添加助剤入 ]? セ メ ン ト系固化材は 、 〔Α〕 水硬性セ メ ン ト 、 〔B〕 硫酸ァ ル ミ 二 ク ム , 明 バン , 硫酸第 1 鉄 , 硫酸第 2 鉄か ら選ばれ る少な く と も 1 種以上の硫酸塩、The cement-based solidifying material is composed of [Α] hydraulic cement, [B] aluminum sulfate, bright ban, ferrous sulfate, and ferrous sulfate. At least one sulfate selected from the group consisting of:
〔c〕 ァ ル カ リ 金属 の炭酸塩 , 重炭酸塩 , 硅酸塩か ら遠ば れ る少 な く と も 1 種以上のア ル カ リ 佥 / ¾ πα 、 〔D〕 ア ル 力 リ 土類金属 の水酸化物ま たば酸化物、 の 4 種の成分か ら 構成 さ れ て お ]? 、 こ れを単独に用 いて有害廃秦物 と 混合 し て も 、 当該有害廃棄物を固化す る と共に、 その中 の有 害污染物質を封 じ込め 固定 し得 る機能を有 し て い る も の であ る ( 特願昭 5 2 - 5 9 8 4 8 号参照 ) が 、 こ の添加 助剤入 セ メ ン ト 系固 化材 と前 δし 曰質を併用 す る こ と に [C] at least one type of alkali metal that is far from carbonates, bicarbonates, and silicates of alkaline metals; It is composed of four kinds of earth metal hydroxides and tobacco oxides.] Even if these are used alone and mixed with hazardous wastes, the hazardous wastes are not It has the function of solidifying and containing and fixing the harmful contaminants contained therein (see Japanese Patent Application No. 52-59884). In addition to the use of cement-based cement containing cement
WA 0WA 0
, て:に, よ ? -、 既存のセ メ ン ト系固化材と脂質を併用す る方法あ るいは、 添加助剤入 セ メ ン ト系固化材のみを用 いる方 法夭 々 の場合の効果から想像される以上の優れた効果が 発揮されるのであ る。 , Then: -The method of using lipid together with existing cement-based solidifying material, or the method of using only cement-based solidifying material with additive aid It is imagined from the effects of premature death More excellent effects are exhibited.
こ の よ う ないわば相乗的効果が得られる理由の全貌は 未だ明 らかでは ないが、 現時点で考え られるひ とつの理 由を以下に示す。 即ち、 油脂が、 セ メ ン ト系固化材の 水和生成物 ( 水酸化 カ ル シ ウ ム ) と反応 して鹼化する こ と に よ 、 有機性有害汚染物質の継続的固定効果を発揮 する と い う こ と は先に述べた と こ ろであ るが、 その場合、 上記鹼化に必要な ア ル力 リ 土類金属の水酸化物はセ メ ン ト系固化材から生成する水和生成物のみから与え られね ばな ら ないから、 その鹼化反応は、 前記水和生成物の生 成を待って時間的及び量的 ¾制約を受けなが ら徐 々 に進 行する こ と に な る。 その点油脂 と前記添加助剤入 ]? セ メ ン ト系固化材を併用 した場合には、 鹼化反応当初か ら 十分な量の アル力 リ 土類金属の水酸化物 ( 前記成分 〔D〕 に含まれ る ) が存在するか ら、 セ メ ン ト系固化材の水和 生 K物の生 Kを待つま で も な く 、 油脂は急速かつ完全に 鹼ィ匕する こ と がで き る こ と に な ]? 、 上記の よ う な優れた 効果が得 られ るので あ ろ う 。  The full reasons why such a synergistic effect can be obtained are not yet clear, but one possible reason at present is as follows. In other words, the fats and oils react with the hydrated product (calcium hydroxide) of the cement-based solidifying agent to be degraded, thereby exhibiting the effect of continuously fixing organic harmful pollutants. As described above, in this case, the alkaline earth metal hydroxide required for the above-mentioned deterioration is generated from cement solidified material. Since it must be provided only from the hydrated product, its oxidation reaction proceeds slowly and in a limited amount of time and quantitatively, waiting for the production of the hydrated product. This will be. When the point oils and fats and the above-mentioned additives are used together, the cement solidifying material is used in combination with a sufficient amount of alkaline metal hydroxide (from the above-mentioned component [D ), The oils and fats can be rapidly and completely removed without waiting for the raw K of the hydrated K material of the cement solidified material. I suppose that the excellent effects as described above can be obtained.
前記添加助剤入 .り セ メ ン ト系固化材 におけ る各成分の 使用量は通常次の一股的な原則に従って決定される。  The amount of each component to be used in the cement-based solidifying material containing the additive is usually determined according to the following general rule.
原則 1 : 成分 〔B〕 .〔C〕 の使用量は相互にほぼ化学反 {&理 Principle 1: The amounts of components [B] and [C] used are almost identical to each other.
O PI O PI
.ィ .. Vv,.·-..,.- 00 ―、^  . ィ .. Vv,. ·-.., .- 00 ― 、 ^
- 論量 に な る こ と。 - Be arguable.
原則 2 : 成分 〔D〕 の使用量は、 少 な く と も 成分 〔B〕,〔C〕 のそれぞれ に対 し て反 、 し得 る化学反応理論量 の和以上であ る こ と σ Principle 2: The amount of the component [D] is low Na rather the well component (B), and anti to pair each, Ru der chemistry than the sum of the theoretical amount that obtained by this [C] σ
原則 3 : 成分 〔Β〕,[: C〕 お よ び 〔D〕 の合計量の水硬性セ メ ン ト 〔A〕 に対する使用割合は 、 無水物換算量 と し てほぼ 0 · 05な い し 1 の範囲 内 であ る こ と。 こ れ らの原則に則って、 固化材中の各成分 〕,〔B〕, 〔C〕,〔D〕 の最適使用量 ¾決定す る こ と がで き るが、 使用 する 水硬性 セ メ ン トの種類、 有害廃秦物中の含水量、 廃 秦物中 に夾雑す る有害汚染物質や水硬 '注セ メ ン トの水和 硬化妨害物質の含有量、 既に始めか ら 混在 し て い る成分 〔B〕,〔C〕,〔D〕 と 同種の物質の含有量 、 な ら びに最終的に 得 ら れ る固化物に期待 さ れ る性能等に 、 じて 適宜 ¾化 さ せれば よ い。 た と えば、 有害廃棄物が、 下水 ス ラ ッ ジ 脱水 ケ - キ等の場合には、 ^過助剤 と し て の石灰が多量 に混在 し て いるの で、 成分 〔D〕 を相当量控除す る こ とが で き る。 ま た、 有害廃棄物が、 金属酸洗 ス ラ ッ ジゃ排 煙脱硫 ス ラ ッ ジ等の場合には、 中和剤 と し て使用 され る 石灰を過刹に含有 し た j? 、 中和生成物 と し て の石膏や金 属塩等を含有す るので、 添加助剤中の各成分の割合を、 こ れ ら含有物質の量'お よ び化学特性を勘案 し て適宜加減 す る こ と 力; で き る。 Principle 3: The ratio of the total amount of the components [:], [: C] and [D] to the hydraulic cement [A] is almost 0 · 05 in terms of anhydride. Must be within the range of 1. In accordance with these principles, the optimal amount of each component in the solidified material), [B], [C], and [D] can be determined. Type, water content in hazardous waste materials, harmful pollutants and hydraulics contaminated in waste materials, hydration of hydraulic cement, content of interfering substances, already mixed from the beginning The content of the same kind of components as [B], [C], and [D], and the performance expected of the finally obtained solidified product, etc., may be appropriately modified. You can do it. For example, if the hazardous waste is sewage sludge dewatering cake, etc., a large amount of lime as a super-aid is mixed, so that the component [D] may be used in a considerable amount. Can be deducted. Also, when the hazardous waste is metal pickling sludge, flue gas desulfurization sludge, etc., lime used as a neutralizing agent was included too much j? However, since it contains gypsum and metal salts as neutralization products, the ratio of each component in the additive is appropriately determined in consideration of the amount and chemical properties of these substances. Ability to adjust;
以上の .如 く 、 本発明 は 、 セ メ ン ト系固化材 ( 最 も 好ま し く は前記添加助剤入 ]5 セ メ ン ト 系固化材 ) に少量の脂 質を併用添加す る だけの極 く 簡単な方法であ って 、 実用 的 に も 、 ま た経済的 に も極め て容易に実施可能な も ので あ ] 3 なが ら、 冒記の従来方法では固定困難であ った有機 性有害物質を も 確実に封 じ込め固定で き 、 し か も 、 その 再溶出 に よ る二次公害の発生 どを招かな い よ う な長期 に亘る極めて優れた封 じ込め固定効果を持続で き る頭著 な利点を有す る も の で あ っ て 、 各種産業に寄与す る工業 的利益は絶大であ る 。 As described above, the present invention provides a cement-based solidifying material (most preferred). This is a very simple method of adding a small amount of fat to the above-mentioned additive-incorporated [5 cement-based solidifying material], and is practically and economically. It is extremely easy to implement.] 3 However, organic harmful substances, which were difficult to fix by the conventional method described above, can be securely contained and fixed. It has a remarkable advantage of being able to maintain a long-lasting, excellent containment and fixing effect that does not cause secondary pollution due to elution. The industrial profits that contribute to the economy are enormous.
な お、 末発明 にお い て使用 さ れ る セ メ ン ト 系固化材 と し て は前記 し た添加助剤入 iP セ メ ン ト 系固化材が最 も好 ま し い こ と は勿論 であ る がそれに限定 さ れ る も の では な く 、 本章前半部 に記述 し た よ う に、 主材に水硬性セ メ ン ト を用 いて い る限 既存の セ メ ン ト系固化材が十分適用 可能であ る こ と は い う ま で も な い。  As the cement-based solidifying material used in the present invention, the above-described iP cement-based solidifying material containing an additive aid is most preferred. However, this is not a limitation, and as described in the first part of this chapter, as long as hydraulic cement is used as the main material, existing cement-based cement Is not always applicable.
ま た、 末発明 で使用 す る セ メ ン ト系固化材 に対 し て、 通常の セ メ ン ト 混和材 も し く は混和材 と し て使用 される 減水剤、 凝結促進剤、 凝結遅延剤、 発泡剤、 起泡剤、 防 水剤、 着色剤、 防かび剤、 防菌剤、 緘維質補強材、 充填 材、 ボ リ マ -質混和材 、 ポ ゾ ラ ン質混和材 、 イ オ ン封鎮 剎、 界面活性剤 、 膨脹材等 々 を 、 .特別に支障の い限 夫 々 の 目 的 に応 じて 併用 で き る。  In addition, a water reducing agent, a setting accelerator, and a setting retarder used as a normal cement admixture or as an admixture with respect to the cement solidification agent used in the present invention. Agents, foaming agents, foaming agents, water-proofing agents, coloring agents, fungicides, antibacterial agents, fibrous reinforcing materials, fillers, polymeric admixtures, pozzolanic admixtures, a On sealants, surfactants, intumescents, etc. can be used in combination depending on the purpose of each, as long as there is no particular problem.
発明 を実施す るための最良の形態 以下 、 末発明方法に よ る纫果を示す代表的 な実 ^例を  BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, representative examples showing the results of the method of the present invention will be described.
OMPI OMPI
\\': 0 挙げるが、 本発明 は、 これ ら実験例 に限定 さ れ る も ので な い こ と は言及す るま で も な い。 . \\ ': 0 However, it should be mentioned that the present invention is not limited to these experimental examples. .
〔 実瞼 ^ 1 〕  [Eyelids ^ 1]
各種の有害汚染物質を含有す る港湾底質 と河川底質の 浚渫汚泥を用 い ( 各浚渫汚泥の含水率お よ び有害汚染物 質含有量は表 1 に示 し て あ るが、 後者の河川底質浚渫 汚 ^の場合には 、 パ ラ チ オ ン お よ び メ チ ル水銀を適当量 添加 し て 、 人工的に さ ら に污染 させて あ る ) 、 末発明に よ る固化材 と 、 既存の セ メ ン ト 系固化材に よ 固化処理 し、 各固化物の一軸圧縮強度 と 有害汚染物質の溶出量を 調べた。 固化 理方法は 、 浚渫汚泥 1 0 0 部 ( 以下、 本明細書 では 、 部 と は総て重量部を意味す る ) を と ? 、 これに既存の セ メ ン ト系固化材に あっ て は先づ 0 · 3 部の 脂質を添加混合 し 、 次で さ ら に 2 0 部の セ メ ン ト系固化 材を添加混合 し た。 こ れ ら の混合物を 日 本工業規格 A 1 1 3 2 「 コ ン ク リ - ト の強度試験供試体の '作 方 」 に準 じ て成形 、 養生、 固化 し て 、 材令 4 週に到達 し た時点 で 日 本工業規格 A 1 1 0 8 「 コ ン ク リ ― ト の圧縮強度試験方 法 」 に準 じ て圧縮強度試験を行な い、 同時に、 固化物に 対 し て 日 本政府環境庁告示昭和 4 8 年 1 3 号 「 産業廃秦 物に含ま れ る有害物質の検定方法 」 ( 痊上埋立処分 ) の その後の改正方法に準 じ て 有害汚染物質の溶出試赣を行 な った。 それ ら の試 結果を纏めて 示す と 表 - 1 の と お であ る o 表 一 Using dredged sludge from harbor sediment and river sediment containing various harmful pollutants (moisture content and harmful pollutant content of each dredged sludge are shown in Table 1, the latter In the case of river sediment dredging, the appropriate amount of parathion and methylmercury is added to artificially further contaminate the riverbed). The material was solidified with the existing cement-based solidified material, and the unconfined compressive strength of each solid and the amount of harmful pollutants eluted were examined. The solidification method is as follows: 100 parts of dredged sludge (hereinafter, “part” means all parts by weight) in the present specification. First, 0.3 parts of lipid was added and mixed, and then, 20 parts of cement solidified material was added and mixed. These mixtures were molded, cured, and solidified in accordance with Japanese Industrial Standards A 1 1 3 2 'How to make concrete strength test specimens', and reached a material age of 4 weeks. At that time, a compressive strength test was conducted in accordance with Japanese Industrial Standard A111, `` Concrete compressive strength test method '', and at the same time, the Japanese government Leaching test of harmful pollutants was carried out in accordance with the subsequent revision of the Environmental Agency Notification No.13, Showa 48, “Testing Methods for Hazardous Substances Contained in Industrial Wastes” (Akagami Landfill). Was. Table 1 summarizes the test results. Table I
Figure imgf000014_0001
Figure imgf000014_0001
河 川 底 質 浚 渫 污 泥 (含水率 6 81o ) River sediment Dredging 泥 Mud (water content 6 81o)
固化物からの有害污染物質の溶出濃度(ppm)または  Elution concentration (ppm) of harmful contaminants from solidified matter or
使 用 固 化 材 一軸圧 原浚渫污泥中の有害汚染物質の含有量(※印のあるもの ppm)  Solidified material used Uniaxial pressure Raw dredging content of harmful pollutants in mud (* marked ppm)
縮強度  Shrink strength
セメン ト系 アルキ 6 ドミ Cement-based archi 6 domi
固化材 脂 質 P C B 有機り λ 総水銀 シアン 価 カ  Solidification agent Fat P C B Organic λ Total mercury Cyanide
'ル水銀 クロム ゥ ム 鉛 砒 素 ホ レトフ  'Le mercury chrome lead Arsenic
ン ドセメン ト ¾ し 3. 5 N D < 0.2 0.001 0.009 N D 0.6 N D 0.07 く 0.05 既存固化材 な し 3. 8 N D < 0.1 < 0.001 0.005 N D 0.07 N D 0.08 N D 添加助剂入り ¾ し 3. 0 N D N D D N D 0.005 N D 固化釗※※※ く 0.001 0.001 N D N  3.5 ND <0.2 0.001 0.009 ND 0.6 ND 0.07 0.05 0.05 No existing solidified material 3.8 ND <0.1 <0.001 0.005 ND 0.07 ND 0.08 ND Additive aid 3. 3.0 NDNDDND 0.005 ND Solidified 釗 ※※※ 0.00 0.001 0.001 NDN
-!-迎ボル トラ -!
ン ドセメン ト 大豆油 3. 3 N D N D N D < 0.001 N D <0.05 N D N D N D 既存固化材 . 同 上 3. 4- N D N D N D < 0.001 N D N D N D N D N D 添加助釗人り 同 上 3. 9 N D N D N D N D N D N D N D N D N D 固化材※※  Cement soybean oil 3.3 N D N D N D <0.001 N D <0.05 N D N D N D Same as existing solidified material Same as above 3.
Λη 原 浚 渫 汚 泥 N D 1 0.1 0.8 1 9 8 0.0 4 7.7 1 0.3 1 2 1 3.8 Λη raw dredged sludge ND 1 0.1 0.8 1 9 8 0.0 4 7.7 1 0.3 1 2 1 3.8
( N Dは検出されなかったことを示す) 乾泥に対す  (ND indicates no detection)
※ 繊維加工用
Figure imgf000015_0001
生廃棄物で、 脂肪酸を主成分とする
* For textile processing
Figure imgf000015_0001
Raw waste, mainly composed of fatty acids
※※ 普通ポルトラン ドセメン ト 8 3部、 硫酸第 1鉄 7水塩 1 2部、 炭酸ソーダ 5部の tt合物と、 消石灰 1 0邵の併用(特隞 5 2 - 5 9 8 48号) ** Ordinary Portland cement 83 parts, ferrous sulfate heptahydrate 12 parts, sodium carbonate 5 parts tt compound and slaked lime 10 shao (Special No. 52-59848)
¾一 1 の結果から、 各種の セ メ ン ト 系固化材に微量の ^質を併用する と、 固化物の一軸圧縮強度の僅か ¾低下 が見られるが 、 有害汚染物質の 定効果は顕著に向上す る こ とがわかる。 と ]9 わけ、 添加助剤入 セ メ ン ト系 固化材と 脂質を併用 した場合の効果は抜群である こ とが わカゝ る o From the results of Example 11, it is found that when a small amount of cement is used in combination with various cement-based solidifying materials, the uniaxial compressive strength of the solidified product is slightly reduced, but the effect of harmful pollutants is significantly reduced. You can see that it improves. 9) In other words, the effect of using a cement-based solidifying material with additive and lipid in combination is remarkable.
〔 秀験例 2 〕  (Excellent example 2)
学名 Da cachlorooc tahyd r o~l .3 · 4— me t e o-2H-cyclob -utaCcdj pentalen-2-one¾ る有機塩素ィ匕合物から る殺 虫剤で汚染された河川底貧の浚渫污泥 〔 含水率 52.5% 、  Scientific name Da cachlorooc tahyd ro ~ l .3 · 4—mete o-2H-cyclob-utaCcdj pentalen-2-one 52.5% moisture content
PH7 -3、強熱滅量 10.5% ( 600C.30 分 ) 、 Ιϋ記有機 ¾素化 合物の含有量 10.2 ppm ( 乾泥に対して ) 〕 を、 既存のセ メ ン ト系固化材ま たは _、 本発明に よ る固化材を用い、 実 験例 1 で示した要 でそれぞれ固化処理 し、 固化物から の前記有核塩素化合物の溶出量を調べた。 その結果を 表一 2 に要約 して示す。 PH7 -3, ignition loss 10.5% (600C for 30 minutes), the content of organic silicon compound 10.2 ppm (based on dry mud)] Each of the solidified materials according to the present invention was subjected to a solidification treatment according to the requirements shown in Experimental Example 1, and the amount of the nucleated chlorine compound eluted from the solidified material was examined. Table 1 summarizes the results.
_0 ΡΙ _0 ΡΙ
Λ, "λζ'ιΡΟ ノ ¾ 0 ■ Λ, "λζ'ιΡΟ ノ ¾ 0 ■
Figure imgf000017_0001
表 1 の注記 と 同 じ
Figure imgf000017_0001
Same as the note in Table 1
表 - 2-の結果から 、 本実験例で用いた ごと き 有機塩素 化合物で汚染された底質浚渫汚泥に対 しては、 セ メ ン ト 系固化材の殆どの も の力;、 それら を単独に用いて固化処 理 して も 、 有機塩素化合物の固定効果は殆んど期待で き ¾いこ と が伴った。 因みに、 未固化の原浚渫汚泥につ いて、 前記有機塩素化合物の溶出試験を行 う と そ の溶 出農度は 5 . 0 p p b であ !) 、 セ メ ン ト 系固化材のみを使用 した多 く の場合がこ の値よ 却って高い値を示した。 これは、 多 く の セ メ ン ト 系固化材がその水和過程でア ル カ リ メ ディ アム を形成 し、 このため、 前記の ごと き有機 塩素化合物の溶解度が増大する こ と に起因する も の と 考 えられる。 一方、 セ メ ン ト 系固化材に微量の脂質を併 用 して固化処理 した も のから は、 総 じて有機塩素化合物 の溶出濃度がいち じる し く 減少 し、 脂質の併用が顕著 固定効果の ある こ と が判った。 From the results in Table 2-, it was found that most of the cement-based solidified material's power against sediment dredged sludge contaminated with organochlorine compounds as used in this experimental example; Even when used alone and solidified, the effect of immobilizing the organochlorine compound was almost expected. By the way, when undissolved raw dredged sludge is subjected to the above-mentioned dissolution test of organochlorine compounds, the leaching agriculture is 5.0 ppb! In many cases, only the cement-based solidified material was used, showing a higher value than this value. This is due to the fact that many cement-based solidifying agents form an alcohol medium during the hydration process, and as a result, the solubility of the organic chlorine compound is increased as described above. It is considered to be something. On the other hand, when the cement solidification material was solidified using a small amount of lipid, the elution concentration of organochlorine compounds decreased significantly, and the combined use of lipid was significantly fixed. It turned out to be effective.
〔 実験例 3 〕  [Experimental example 3]
PCB で汚染された港湾底質浚渫汚泥 〔 PCB含有量 239 p pm ( 乾泥に対 して ) 、 含水率 78 % 、 強熱減量 3 5%〔600 V . 30分 ) 、 PH 7 . 8 〕 を用い、 本発明に よ る固化材の脂 質の使用条件を種々 に変えた場合の P C B の固定効果に 及ぼす影響を調べた。 セ メ ン ト 系固化材には前記実験 例 1 で示 した添加助剤入 J 固化剤を選'び、 これを浚渫汚 泥 1 0 0 部に対 して 2 5 部使用 し、 脂質の併用は、 そ の 種類、 状態、 添加順序、 添加量を種々 に変えて行 つた P C B の溶出試験は、 常温湿空中で養生 した固化物につ て、 その材令 2 週お よび 4 週において実験例 1 で述べ た日本政付環境庁告示の方法に準じて行った。 これら の実験結果を要約 して示す と表一 3 の と お り であ る。 Port sediment dredged sludge contaminated with PCB [PCB content: 239 ppm (relative to dry mud), water content: 78%, ignition loss: 35% [600 V, 30 minutes], PH 7.8] The effect of changing the use conditions of the fat of the solidified material according to the present invention on the PCB fixing effect was examined using the above method. For the cement-based solidifying material, select the J-solidifying agent containing the additive aid shown in Experimental Example 1 above, and use 25 parts of this for 100 parts of dredged sludge, and also use lipid together. Was carried out by changing the kind, condition, order of addition and amount of addition. The dissolution test of the PCB was performed on the solidified material cured in a room-temperature, humid air at 2 weeks and 4 weeks of material age according to the method of the Notification of the Environment Agency of Japan, mentioned in Experimental Example 1. Table 13 summarizes the results of these experiments.
O
Figure imgf000019_0001
※ そ のま ま : そ のま ま の状態
O
Figure imgf000019_0001
* As it is: As it is
エ マ ノレ シ 3 ン : 非ィ オ ン 糸界面活性剤を用 い て、 正味  Emanoresin: non-ionic yarn surfactant, net
脂質濃度 2 0 の水中エ マ ノレ ジ ョ ン と した も の  Ethanol in water with lipid concentration of 20
サスペン ジ ョ ン : 正味脂質 2 0 、 ベ ン ト ナ イ ト 2 0 % 水 6 0 の組成物に少量の非ィ オ ン 系 界面活性剤を加えて攪拌混合 し、 サ ス ペ ン ジ ョ ン と し た も の  Suspension: A small amount of a nonionic surfactant is added to a composition of net lipid 20 and bentonite 20% water 60, and the mixture is stirred and mixed. What I did
ブレ ミ ックス ト : 大豆油を所定濃度でセ メ ン ト 系固化材  Blemix: Cement-based solidifying material with soybean oil at a specified concentration
中に混和 して分散さ せ、 ブレ ミ ッ ク ス ト の固化材と ¾ した も の  It is mixed with and dispersed inside, and is used as a solidifying material for blemix.
« ※事前添加 先づ脂質を浚渫汚泥に添加混合 し、 次に  «* Pre-addition First add and mix lipids into dredged sludge, then
セ メ ン ト 系固化材を添加混合する  Add and mix cement solidification material
同時添加 脂質と セ メ ン ト 系固化材を同時に浚渫污  Simultaneous addition Dredging of lipid and cement-based solidified material simultaneously.
泥に添加 し て混合するか、 脂質と セ メ ン ト 系固化材と を ブレ ミ ッ ク ス した も の を 浚渫汚泥中に添加混合する 。  Add to and mix with mud, or add and mix blemishes of lipid and cement-based solidifying material into dredged sludge.
事後添加 事前添加の逆の順序で添加混合する  Post-addition Add and mix in reverse order of pre-addition
表 - 3 の結果から 、 脂質の種類、 その状態およ び.添加 順序は、? C B の固定効果にほと ん ど影響を与え いが、 脂質の添加量を或る限度以下に減らすと効果が低下する こ と がわかった。 しカゝ しながら 、 実質的には、 脂質の 添加量がきわめて微量であって も 有効である と言える。  Based on the results in Table-3, the type of lipid, its state, and the order of addition are as follows: It has little effect on the fixation effect of CB, but it was found that the effect decreased when the amount of lipid added was reduced below a certain limit. However, it can be said that practically even if the amount of lipid added is extremely small, it is effective.
__ΟΜΡΙ___ΟΜΡΙ_
, "wipo _^y 産業上の利用可能性 , "wipo _ ^ y Industrial applicability
以上に記載の各実験例において 、 その有用性が証明 さ れた通 ]? 、 本発明は、 有害廃棄物中の重金属類のみ ら ず、 従来のセ メ ン ト 系固化材の単独使用では固定困難で あった有機性の有害汚染物質を も 、 再溶出に.よ る二次公 害の発生な どの心配が い程度に封 じ込め固定で き る非 常に勝れた特徵を有し、 しか も 、 本発明に:おいて新た.に 追加併用する に至った脂質には—、 比較的入手が容易: ¾ も のが多 く 、 それ故に、 実用的に も 、 経済的に も極めて容 易に実施可能であ 、 その工業利益は絶大なる も の力;あ o  In each of the experimental examples described above, its usefulness was proved.] However, the present invention is not limited to heavy metals in hazardous wastes, but can be fixed by the conventional cement-based solidifying material alone. Organic harmful contaminants, which had been difficult, can be contained and fixed to the extent that there is no need to worry about the occurrence of secondary pollution due to re-elution. Also, in the present invention, the lipids newly added to be used in combination are relatively easily available: ¾ Many are available, and therefore, both practical and economical are extremely easy. And its industrial benefits are enormous;

Claims

/01249 / 01249
(20) (20)
5冃 小 の 範 囲  5 冃 Small range
物剤はあしし  Stuff
① 有害汚染物質を含有する有害廃棄物を固化する方法 で あって、 Ιϋ記有害廃秦物に、 水硬性セ メ ン ト も し く は水硬性を有する セ メ ン ト質を 主 分 とする セ メ ン ト 固化材と 脂質を、 同時にま たは別々 に添加混合 して 化する と と も に、 前記有害汚染物質を封 じ込め固定 する こ と を特徵 とする。  ① This is a method of solidifying hazardous waste containing hazardous pollutants. Ιϋ Hydraulic cement or hydraulic cement is mainly used for hazardous waste. It is characterized in that a cement solidifying material and a lipid are simultaneously or separately added and mixed, and that the harmful contaminants are sealed and fixed.
② 特許請求の範囲第①項に記載の方法であって、 前記 したセ メ ン ト 系固化材が下記の成分か ら 搆成 される も のである 〔Α〕 水硬性セ メ ン ト 、 〔Β〕 硫酸ア ル ミ 二 ク ム 、 明パン 、 硫酸第 1 鉄、 硫酸第 2鉄から還ばれる 少る く と も / 種以上の硫酸塩、 〔C〕 ァ ノレ 力 リ 金属の炭 塩、 重炭酸塩、 硅酸塩か ら選ばれる少な く と も /種 以上のア ル 力 リ 金属塩、 〔D〕 ア ル 77 リ土镇金^の水酸 化物ま たは酸化物。 特許請求の範 1¾第②項に記載の万法であって、 前記 た脂貧は 、 脂肪油ま たは脂肋'酸、 或いは両者の混合 、 若し く は これ ら を主成分 と する も のであ る。 特許請求の範囲第③項に記載の方法であって、 fir記 た脂質は、 粗製品ま たは廃食用油、 若 し く は各種油 製造適程ま たは油精製過程等で副生する ^肪油ま た 脂肪酸を含む廃棄物でめ る。 特許請求の範囲第 項ま たは第^:'項に記 «の万法で つて、 前記セ メ ン ト 糸固化材中の跃分 〔A〕 ,に対する (2) The method according to the above (1), wherein the cement-based solidifying material is formed from the following components: [Α] hydraulic cement, [Β At least one or more sulfates returned from aluminum sulfate, light brown bread, ferrous sulfate, and ferrous sulfate; (C) carbonaceous metal, bicarbonate At least one or more kinds of metal salts selected from the group consisting of salts and silicates; [D] hydroxides or oxides of Al77 lithium earth metal. The method according to claim 1, wherein the fat or oil is a fatty oil or a fatty acid, or a mixture of the two, or a mixture of both. It is. The method according to claim 3, wherein the lipid described in fir is a by-product in crude product or waste edible oil, or in an appropriate amount of oil production or in an oil refining process. ^ Waste products containing fatty oils and fatty acids. According to the method described in claims or ^: ', the content of the cement yarn solidified material [A],
_Ο Ρ1_ ' . 一 W1PO \ U A T /01249 _Ο Ρ1_ '. One W1PO \ UAT / 01249
(21) (twenty one)
分 〕 , 〔C〕 , ( D) の合計量が無水物換算量 と して 約 0 .05 ない し 1 に る よ う に ¾成 され る こ と を特徴 とする。  ), [C], and (D) to be about 0.05 or 1 in terms of anhydride.
⑥ 特許請求の範 第⑤項に記載の方法であって、 前記  方法 The method of claim 1 wherein the method
有害廃棄物等 φにすでに前記セ メ ン ト系固化材中の成 分 〔Β〕 , 〔C〕 , 〔D〕 のそれそれ と 同種の物質が存在 し ている場合に、 その存在量に見合 う 量の前記成分を、 前記セ メ ン ト系固化材か ら控除する こ とを特徴と する。 Hazardous waste, etc. If the same kind of substances as those of components [Β], [C], and [D] in the cement-based solidified material already exist in φ, the amount is considered to be present. The amount of the component is reduced from the cement-based solidified material.
⑦ 特許請求の範 ia第⑥項に記載の方法であって、 前記 方法 The method of claim ia, wherein the method comprises:
した脂質は有害廃棄物の重量に対し て約 10,000 分の 1 る い し 2 0 分の 1 の量を 加混合する こ と を特徴 と する 。  The lipids are characterized in that about 1 / 10,000 or 1/20 of the weight of hazardous waste is added and mixed.
_ OMP1一_ OMP1
- WiPO ノ  -WiPO ノ
PCT/JP1978/000062 1978-12-20 1978-12-20 Solidification of harmful solid waste WO1980001249A1 (en)

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Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE1300856B (en) * 1965-11-25 1969-08-07 Teutonia Cementwerk Process for the production of hydrophobic cement
DE1804419A1 (en) * 1968-10-22 1970-05-21 Dyckerhoff Zementwerke Ag Procedure for eliminating oil plague
US3547665A (en) * 1967-06-21 1970-12-15 Fats & Proteins Res Found Additive for concrete,mortar and other cementitious mixtures
JPS5060469A (en) * 1973-09-29 1975-05-24
JPS5074569A (en) * 1973-11-02 1975-06-19
JPS50137871A (en) * 1974-04-25 1975-11-01
JPS537728A (en) * 1976-07-12 1978-01-24 Denki Kagaku Kogyo Kk Hardening agent for sludge
JPS5315987B2 (en) * 1975-02-21 1978-05-29
JPS5342315B2 (en) * 1974-12-13 1978-11-10

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE1300856B (en) * 1965-11-25 1969-08-07 Teutonia Cementwerk Process for the production of hydrophobic cement
US3547665A (en) * 1967-06-21 1970-12-15 Fats & Proteins Res Found Additive for concrete,mortar and other cementitious mixtures
DE1804419A1 (en) * 1968-10-22 1970-05-21 Dyckerhoff Zementwerke Ag Procedure for eliminating oil plague
JPS5060469A (en) * 1973-09-29 1975-05-24
JPS5074569A (en) * 1973-11-02 1975-06-19
JPS50137871A (en) * 1974-04-25 1975-11-01
JPS5342315B2 (en) * 1974-12-13 1978-11-10
JPS5315987B2 (en) * 1975-02-21 1978-05-29
JPS537728A (en) * 1976-07-12 1978-01-24 Denki Kagaku Kogyo Kk Hardening agent for sludge

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