JP2006247645A - Modification treatment agent, modification treatment method of heat history silicate and binding shape body modified it - Google Patents

Modification treatment agent, modification treatment method of heat history silicate and binding shape body modified it Download PDF

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JP2006247645A
JP2006247645A JP2005380986A JP2005380986A JP2006247645A JP 2006247645 A JP2006247645 A JP 2006247645A JP 2005380986 A JP2005380986 A JP 2005380986A JP 2005380986 A JP2005380986 A JP 2005380986A JP 2006247645 A JP2006247645 A JP 2006247645A
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water
silicate
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Hiroyuki Naito
博之 内藤
Nanae Naitou
七絵 内藤
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NATOO KENKYUSHO KK
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NATOO KENKYUSHO KK
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<P>PROBLEM TO BE SOLVED: To provide a technique related to a modification treatment agent capable of recycling wastes as regenerating materials in a low cost without giving burden to environment and detoxifying injurious substances in a functional technique and an environmental problem which are retained by a hydraulic solidifying agent widely used as an ordinary technique. <P>SOLUTION: This technique provides: a "modification treatment method" for applying a detoxifying treatment and a shape forming treatment by adding a "modification treatment agent" which exceeds pH 12 modifying wastes comprised of a heat history silicate constituted with dormant components, the heat history silicate via water-based solvent, and a series of working processes which make effective use of the modification treatment agent at least at a normal temperature to the wastes coexisting with the injurious substances; and "binding shape body", in which the detoxifying treatment and the shape forming treatment are applied, as water resistance regenerating materials which are secured less than pH 10 and not be re-sludged underwater by adding the modification treatment method to the wastes coexisting with injurious materials. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、改質処理剤、熱履歴シリケートの改質方法ならびに熱履歴シリケートが改質された結着形状体に関する。より詳細には、休眠成分で構成される熱履歴シリケートからなる廃棄物類を改質処理するpH12を超える「改質処理剤」、水系溶媒を介して熱履歴シリケート、特に有害物質を共存する廃棄物類に改質処理剤を少なくとも常温で活用処理せしめる一連の作業工程に付して無害化処理ならびに形状化処理を施す「改質処理方法」、ならびに有害物質を共存する廃棄物類に改質処理方法を付してpH10未満が確保されて水中で再泥化しない耐水性の無公害型再資源化資材とする無害化処理ならびに形状化処理が施されている「結着形状体」を提供する技術にある。  The present invention relates to a modification treatment agent, a method for modifying a heat history silicate, and a binding shape body having a heat history silicate modified. More specifically, a “reforming agent” exceeding pH 12 for reforming wastes composed of heat history silicate composed of dormant components, waste that coexists with heat history silicates, particularly harmful substances, through an aqueous solvent. "Reforming treatment method" that applies detoxification treatment and shaping treatment to a series of work processes that allow substances to be used and treated at least at room temperature, and reforms to waste that coexists with harmful substances Providing a “bounded shape body” that has been subjected to detoxification treatment and shaping treatment as a water-resistant, non-polluting recyclable material that has a pH of less than 10 and is not re-mudged in water. There is technology to do.

さらに本発明においては、休眠成分で構成される熱履歴シリケートを改質対象素材として、pH12を超える改質処理剤ならびに必要に応じて機能付与剤を併配合して水を介して調製される活性化混和物、ないしは加工形状化された形状化処理物もしくは応用対象基材の表面上に加工付着化された付着化処理物を少なくとも常温に雰囲気中に開放せしめて結着形状体とする一連の作業工程により改質処理されている再資源化資材である原位置非成型品、耐水性粉粒体品ないしは形状加工成型品、もしくは応用対象基材と一体化された結着成型活性品、基材積層複合品、顆粒群体集合品ないしは注充填一体化品を工業用資材、建築・土木資材、生活関連資材、植物育成資材、環境対応資材ないしは趣向活資材として各種用途に提供される結着形状体に関する。  Furthermore, in the present invention, a heat history silicate composed of a dormant component is used as a material to be modified, and an activity prepared via water by combining a modifying agent exceeding pH 12 and a function-imparting agent as necessary. A series of shaped admixtures, or shaped processed products that have been processed into shapes, or processed processed adhering materials on the surface of the substrate to be applied, are released into an atmosphere at least at room temperature to form a bound shape. In-situ non-molded product, water-resistant granular product or shape-processed molded product that is a recycled material that has been modified by the work process, or a binder molding active product that is integrated with the target substrate Bonded materials provided for various uses as laminated materials, granule aggregates or injection-filled integrated products as industrial materials, construction / civil engineering materials, life-related materials, plant growth materials, environmentally friendly materials or preference materials Body on.

本発明に係わる一般的な背景技術は、常温で水硬性を発揮する無機質系の固化材、硬化剤、結着剤、バインダー等の改質処理剤を活用して調製される固化体、硬化体、結着体等関連する技術分野にある。さらに本発明に係わる特長的な背景技術は、ケイ酸塩系化合物からなる休眠成分で構成される熱履歴シリケート、特に廃棄物類を結着形状体として再生利用する技術ならびに廃棄物類に共存する有害物質、特に溶出する共存重金属類の不溶化処理技術にある。これら背景技術に社会が求めている環境に低負荷型で省エネ型を可能とし、低コストで環境を安全に改善・保全できる技術にある。  The general background art related to the present invention is a solidified body and a hardened body prepared by utilizing an inorganic solidifying material that exhibits hydraulic properties at room temperature, a curing agent, a binder, a binder, and the like. In related technical fields such as binders. In addition, the characteristic background art relating to the present invention is coexisting in heat history silicate composed of a dormant component composed of a silicate compound, in particular, technology for recycling and recycling wastes as bound shapes and wastes. It is in the insolubilization treatment technology for harmful substances, especially coexisting heavy metals. These background technologies lie in the technology that enables low-load and energy-saving in the environment demanded by society, and can safely improve and maintain the environment at low cost.

特に廃棄物類の処理・処分は、循環型社会の構築が提案されていることもあり、再生利用を軸として人の健康ならびに動植物に悪影響を与えず、充分に環境が保護される条件下において処理・処分されることが大前提である。したがって、廃棄物類に含有する有害物質が生活環境に拡散汚染することは許されず、法の定める環境基準を尊守できない処理・処分ならびに処理手段は厳しく禁じられており、地球温暖化への対応もあり、環境に低負荷型を可能とする廃棄物類の低コスト再生利用技術が求められている。  In particular, the construction and recycling of wastes has been proposed for the treatment and disposal of wastes, and under conditions where the environment is adequately protected without adversely affecting human health and animals and plants, centering on recycling. The main premise is that it will be treated and disposed of. Therefore, hazardous substances contained in wastes are not allowed to diffuse and contaminate the living environment, and treatment, disposal and treatment methods that cannot respect the environmental standards stipulated by the law are strictly prohibited. There is also a need for a low-cost recycling technology for waste that enables a low-load environment.

したがって、背景技術において示されるように廃棄物類に共存するダイオキシン類または有害な元素群等の有害化学物質が生活環境ならびに人の健康に悪影響を与えている現実を直視し、環境に関する法律『環境基本法』および関連する命令、告示、条例等で示される「人の健康を保護し、生活環境を保全する上で維持することが望ましい基準」に対処でき、人類の生活環境の保全・改善を可能とする処理技術の開発は重要である。  Therefore, as shown in the background art, we faced the reality that dioxins coexisting in wastes or harmful chemical substances such as harmful elements are adversely affecting the living environment and human health. It is possible to protect and improve the living environment of mankind by addressing the “standards that are desirable to protect and protect the human health and protect the living environment” indicated in the “Basic Law” and related instructions, notifications, ordinances, etc. It is important to develop processing technology.

現在、一般廃棄物ないしは産業廃棄物の中でもケイ酸塩化合物を主成分とするゴミ、汚泥、燃え殻(焼却灰)等の不要物の処理・処分は、一般的に特定管理区域とされる埋立地に投棄・埋立することにより処分されてきた。しかし現在、廃棄物類、特に有害な元素類やダイオキシン類を共存していて放出・拡散せしめする廃棄物類を投棄・埋立する投棄場所や埋立地の確保は困難となり、また現状の社会環境ならびに生活環境において廃棄物類が受け入られる状況は大変困難な状況にある。したがって今後、有害元素類を溶出し、またダイオキシン類を放出する廃棄物類等を投棄・埋立により処理・処分する手段・方法は社会が許さない状況にある。  Currently, landfills that are generally designated as specially managed areas are used for the disposal and disposal of waste, sludge, husks (incineration ash), etc., which are mainly silicate compounds among general and industrial waste. It has been disposed of by dumping and landfilling. At present, however, it is difficult to secure a dumping site or landfill site for dumping / landfilling wastes, especially wastes that are coexisting with harmful elements and dioxins and are released and diffused. The situation where waste is accepted in the living environment is very difficult. Therefore, in the future, there will be no way for society to allow means and methods for treating and disposing of wastes that elute harmful elements and release dioxins by dumping or landfill.

有害な元素類
以上の状況から、当然、廃棄物類等、特にケイ酸塩化合物を主成分とする廃棄物類は、一般に有害な元素類を含有して溶出することから、環境庁は、「重金属等に係る土壌汚染調査・対策指針及び有機塩素系化合物等に係る土壌・地下水汚染調査・対策暫定指針」(平成6年指針)を全面的に改定し、新たに「土壌・地下水汚染に係る調査・対策指針」及び同運用基準を策定し、都道府県、関係省庁等に対し通知し、定義している。これらの法律における環境基準で対象とされる有害な元素群としては、カドミニウム、砒素、水銀、鉛、クロム、セレン、ホウ素、フッ素が挙げられている。
Hazardous elements From the above situation, of course, wastes, especially wastes that are mainly composed of silicate compounds, generally contain harmful elements and are eluted. Guidelines for soil contamination surveys and countermeasures related to heavy metals, etc., and provisional guidelines for soil and groundwater contamination surveys and countermeasures related to organochlorine compounds, etc. (1994 Guidelines) have been completely revised. The “Survey / Countermeasure Guidelines” and the operational standards were formulated and notified to prefectures and related ministries and agencies. Hazardous element groups covered by environmental standards under these laws include cadmium, arsenic, mercury, lead, chromium, selenium, boron, and fluorine.

ダイオキシン類
また、PCBを含めたダイオキシン類は、1999年には新しい環境基準が設定され、土壌の基準を1000pg/gとし、250pg/gを調査指標とし、特に焼却施等でこれを超える場合は、直ちに除去などの対策を取ることが規制されている。また、ダイオキシン類対策特別措置法の規制対象となる廃棄物焼却炉の集じん機で集められたばいじんおよび焼却灰・他の燃え殻の処分を行う場合には、含むダイオキシン類の量が、ばいじんおよび焼却灰その他の燃え殻1gにつき3ng−TEQ以内となるよう処理する必要があるとしている。一方、水質の環境基準は、1pg/リットルとしている。また、ゴミ焼却施設、下水道終末処理施設、紙パルプ製造業、塩化ビニル製造施設等では、10pg/リットルとしている。大気については0.6pg/mに強化されている。
Dioxins Also, new environmental standards for dioxins including PCBs were set in 1999. The soil standard was set to 1000 pg / g, and 250 pg / g was used as a survey index. Measures such as immediate removal are regulated. In addition, when disposing of dust collected from incinerator dust collectors and incineration ash and other husks subject to regulation under the Special Measures Law for Countermeasures against Dioxins, the amount of dioxins contained is It is said that it is necessary to treat the incinerated ash and other burning hu to be within 3 ng-TEQ per 1 g. On the other hand, the environmental standard for water quality is 1 pg / liter. In addition, in garbage incineration facilities, sewerage end treatment facilities, paper pulp manufacturing industry, vinyl chloride manufacturing facilities, etc., the rate is 10 pg / liter. The atmosphere is enhanced to 0.6 pg / m 3 .

しかし一方、廃棄物等の処理に関しては、「廃棄物の処理及び清掃に関する法律」(廃掃法)に規制されており、現在廃棄物等の処理・処分方法は、特定管理区域への投棄・埋立が一般的であるが、工夫されている処理・処分方法としては、廃棄物類を▲1▼溶融スラグ化して、タイル、ブロック、煉瓦、粗骨材、撒き砂等に供給、▲2▼セメント等の固化剤による成型固化技術によりタイル、ブロック、煉瓦、軽量骨材等に供給、▲3▼セメント製造副資材、土壌改良材等に供給する方法等が採択されて一部再生利用されている。  However, the disposal of waste, etc., is regulated by the “Act on Waste Disposal and Cleaning” (Waste Removal Law). Currently, the disposal and disposal methods for waste, etc. are dumped and landfilled in specific management areas. However, as a well-developed treatment / disposal method, wastes are converted into (1) molten slag and supplied to tiles, blocks, bricks, coarse aggregate, sand, etc., (2) cement Supplying to tiles, blocks, bricks, lightweight aggregates, etc. by molding solidification technology using a solidifying agent such as (3) A method of supplying to cement production secondary materials, soil improvement materials, etc. has been adopted and partially recycled .

しかるに溶融スラグ化方法は、一旦焼却処理した焼却灰を溶融せしめるために高温を必要とする。その結果、大切な熱エネルギー資源を多量に消費し、しかも二酸化炭素を多量に放出することから、熱エネルギー資源の確保ならびに地球温暖化対策に課題を残している。しかも、溶融スラグ化方法では、高温での熱処理が必要であることから、高価な溶融設備ならびに排気ガス処理設備を必要とし、溶融スラグ化方法では低コス・低負荷型での焼却灰処理は望めなく、焼却灰を安価な処理物とする供給は困難である。  However, the molten slag method requires a high temperature to melt the incinerated ash once incinerated. As a result, it consumes a large amount of important thermal energy resources and releases a large amount of carbon dioxide, leaving challenges for securing thermal energy resources and combating global warming. Moreover, since the molten slag method requires heat treatment at high temperatures, it requires expensive melting equipment and exhaust gas treatment equipment, and the molten slag method can be used for incineration ash treatment with low cost and low load. Therefore, it is difficult to supply incinerated ash as an inexpensive processed product.

また、セメント等の固化剤による成型固化方法では、セメントが本質的に有害な六価クロムを含有しており、二次製品等からの廃棄物類溶出の有害元素類に加えて有害な六価クロムを生活環境に拡散汚染させている実態は免れない。また、セメント混和剤等への製造副資材原料としての供給も、昨今の公共工事の低迷等からくるセメント需要の先行きにも陰りがあり、セメント業界で焼却灰を大量処理するには自ずと制限があり、セメント業界が廃棄物類を大量に処理・利用する将来性に多くの期待は望めない。  In addition, in the molding and solidification method using a solidifying agent such as cement, the cement contains hexavalent chromium which is essentially harmful, and in addition to the harmful elements eluted from secondary products, harmful hexavalent The fact that chrome is diffused and contaminated in the living environment is inevitable. In addition, the supply of raw materials for manufacturing admixtures to cement admixtures and other factors has a negative impact on the future demand for cement resulting from the slowdown of public works in recent years. There are many expectations for the future of cement processing and using a large amount of waste.

また、ダイオキシン類は、一般には、450ないしは500℃以上の温度に曝露することにより分解無害化されルことから、これ以上の温度にて分解されているが、分解ガス成分が分解ガスの冷却時に冷却雰囲気中で再度ダイオキシンを合成する傾向にあり、単にダイオキシンを燃焼すれば無害化される状態にはない。したがって、チタニヤやバナジウム系等の各種の触媒等を併用して無害化を行ってが、特別な高価な装置を必要としており、安価な処理方法とはなっていない。また、ダイオキシン類を低温で分解する技術も開示されているが、多くは特別に選択された微生物の菌類や酵素を用いて、月単位の時間をかけ分化しており、経済的ではない。  In general, dioxins are decomposed and detoxified by exposure to a temperature of 450 to 500 ° C. or higher, so that they are decomposed at a temperature higher than this. There is a tendency to synthesize dioxin again in a cooling atmosphere, and if dioxin is simply burned, it is not in a detoxified state. Therefore, detoxification is performed using various catalysts such as titania and vanadium in combination, but a special expensive apparatus is required, and it is not an inexpensive treatment method. Although a technique for decomposing dioxins at a low temperature has been disclosed, many are differentiated over a period of months using specially selected microorganisms or enzymes, which is not economical.

以上の状況から、次世代の廃棄物類の確かな処理供給先を確保する案件は重要な課題である。特に廃棄物類から溶出する有害な元素類やダイオキシン類を生活環境に拡散汚染しない方法・手段により、廃棄物類を処理・処分する技術を確立することは大切であると判断される。こうした中で既に過去に数々の処理・処分に係る技術が開示され、多くの研究ならびに発明技術が開示されており、これらから学ぶところが多い。  From the above situation, a project to secure a reliable processing and supply destination for next-generation wastes is an important issue. In particular, it is judged to be important to establish technology for treating and disposing of wastes by methods and means that do not diffuse and contaminate harmful elements and dioxins that are eluted from wastes into the living environment. Under these circumstances, a number of technologies relating to treatment and disposal have already been disclosed in the past, and many researches and invention technologies have been disclosed.

従来技術において、廃棄物類から溶出する8種類の有害元素(カドミニウム、砒素、水銀、鉛、クロム、セレン、ホウ素、フッ素)を個別に処理対象として固定・不溶化する処理技術は、発明技術としても多く開示されている。特に、生活環境に悪影響を及ぼす水可溶性の重金属類の無害化処理技術としては、水可溶性重金属類で汚染されている土壌地盤や廃棄物類を処理対象にして、系外から薬剤や処理剤を添加配合して、水可溶性重金属類を不溶化処理する技術が多く開発され、開示されている。しかし、これらの技術において、処理対象とする素材の成分を活用して効率よく水可溶性の有害な重金属類ならびに有害なホウ素やフッ素の酸類元素を不溶化処理する技術の開示はない。  In the conventional technology, the processing technology that fixes and insolubilizes 8 types of harmful elements (cadmium, arsenic, mercury, lead, chromium, selenium, boron, fluorine) that are eluted from wastes individually as the processing target Many have been disclosed. In particular, as a detoxification treatment technology for water-soluble heavy metals that adversely affect the living environment, the soil ground and wastes contaminated with water-soluble heavy metals are treated, and drugs and treatment agents are applied from outside the system. Many techniques for adding and blending to insolubilize water-soluble heavy metals have been developed and disclosed. However, in these techniques, there is no disclosure of a technique for efficiently insolubilizing harmful heavy metals that are water-soluble and harmful boron and fluorine acids by utilizing the components of the material to be treated.

しかも以上8種類の有害元素は基本的にそれぞれ異なる性状を示すことから、異なる8種類の有害元素を単一の単純処理材で一括して全て少なくとも常温で固定・不溶化する処理技術の開示はなく、異なる8種類の有害元素、特にホウ素やフッ素の酸類元素を重金属類を区別することなく同時に単一の単純処理材により常温で安定して安全に固定・不溶化する処理技術は求められている。  In addition, since the above eight types of harmful elements basically have different properties, there is no disclosure of a processing technique that fixes and insolubilizes all eight different types of harmful elements in a single simple processing material at least at room temperature. Thus, there is a need for a processing technique for stably fixing and insolubilizing eight different types of harmful elements, particularly boron and fluorine acids, at the same time by using a single simple processing material without distinguishing heavy metals.

重金属類を固定・不溶化する代表的な処理技術として、1)廃水処理を伴うが水等により重金属類を洗浄処理する技術、2)排気処理を伴うが重金属類を熱分解によりヒューム化して回収処理する技術、3)キレート等の薬剤配合による重金属類を水不溶性にキレート化処理する技術、4)セメント等により重金属類を被覆処理する技術等を挙げることができる。中でも、処理費等の関係から薬剤や処理材により重金属類を固定・不溶化せしめる技術の開示は多い。  Typical treatment technologies for fixing and insolubilizing heavy metals: 1) Technology that involves wastewater treatment but cleans heavy metals with water, etc. 2) It involves exhaust treatment, but fumes are recovered by pyrolysis of heavy metals. 3) a technique for chelating heavy metals with a chemical compound such as a chelate, and 4) a technique for coating heavy metals with cement or the like. In particular, there are many disclosures of techniques for fixing and insolubilizing heavy metals with chemicals and treatment materials due to treatment costs.

最近は、ホウ素ないしはフッ素を水に不溶化せしめる処理技術も多くに開示されており、例えば、特開2004−283787等においては、汚染物物質を含む土壌に対して、セメント、消石灰等のカルシウム系材料による処理;リン酸塩、炭酸塩、硫化物塩等の陰イオン系材料;第一鉄塩、第二鉄塩、アルミニウム塩等の金属イオン系材料による処理;金属鉄、金属アルミニウム、金属亜鉛等の金属材料による処理;ジアルキルジチオカルバミン酸等のキレート系材料;アパタイト、ゼオライト等の無機系吸着材による処理;イオン交換樹脂による処理;イミノ二酢酸等の官能基を有するキレート樹脂による処理等の不溶化処理技術が開示されている。  Recently, many treatment techniques for insolubilizing boron or fluorine in water have been disclosed. For example, in Japanese Patent Application Laid-Open No. 2004-283787, a calcium-based material such as cement or slaked lime is used for soil containing contaminants. Treatment with metal ion-based materials such as ferrous salts, ferric salts, aluminum salts; metal iron, metal aluminum, metal zinc, etc. Treatment with metal materials; Chelate materials such as dialkyldithiocarbamic acid; Treatment with inorganic adsorbents such as apatite and zeolite; Treatment with ion exchange resins; Treatment with chelating resins having functional groups such as iminodiacetic acid Technology is disclosed.

特開2004−089816においては、フッ素あるいはホウ素が溶出する土壌またはフッ素、あるいはホウ素が溶出する焼却灰に対して、水硬性結合材として選択したであるポルトランドセメント、混合セメント、エコセメント、特殊セメント、酸化マグネシウム、マグネシアセメント、石灰等、もしくはさらにカルシウム塩を配合した水硬性結合材を添加、混合することにより、溶出するフッ素あるいはホウ素を不溶化せしめる技術を開示している。しかし、処理対象物をセメントで活性化される技術開示はない。  In JP-A-2004-089816, Portland cement, mixed cement, eco-cement, special cement, which is selected as a hydraulic binder for soil from which fluorine or boron elutes or fluorine or incinerated ash from which boron elutes, A technique for insolubilizing eluted fluorine or boron by adding and mixing a hydraulic binder containing magnesium oxide, magnesia cement, lime or the like or further containing calcium salt is disclosed. However, there is no technical disclosure that activates the object to be treated with cement.

さらに廃棄物類から溶出する有害な元素群として、フッ素あるいはホウ素を特定することなくカドミニウム、砒素、水銀、鉛、クロム、セレン等の重金属群を固定化して水不溶化せしめる処理技術の代表的な技術開示は、例えば、特開平09−155319に開示されている炭酸アルカリと硫酸第一鉄、硫酸アルミニウム、さらにセメントを下水汚泥焼却灰に加えて混練・固化させて溶出する重金属類を不溶化させる技術、また特開2003−175370、特開2002−001273、特開2000−279971等の公開特許には、硫酸第一鉄等の鉄塩を下水汚泥焼却灰に加えて混練・固化させて、溶出する重金属類を不溶化させる技術が開示されている。  Furthermore, as a harmful element group that elutes from wastes, a representative technology of treatment technology that immobilizes heavy metal groups such as cadmium, arsenic, mercury, lead, chromium, selenium, etc., without specifying fluorine or boron, and insolubilizes them. Disclosure is, for example, an alkali carbonate and ferrous sulfate disclosed in JP-A-09-155319, a technique for insolubilizing heavy metals that are eluted by kneading and solidifying by adding cement to sewage sludge incineration ash, Also, published patents such as JP2003-175370, JP2002-001273, JP2000-279971, etc. describe heavy metals that elute by adding iron salt such as ferrous sulfate to sewage sludge incineration ash and kneading and solidifying it. A technique for insolubilizing a kind is disclosed.

また、本発明者等による先願技術(特開平12−263661)には、シラノール基を有するシリカーアルカリ組成物とアルカリ土類金属のアルミン酸組成物を水に分散せしめた湿式流動体で粉状体でない水硬性シリカ系バインダーが開示されている。さらに、本発明者等による先願技術(特開2002−128550)には、ケイ酸塩系素材100質量部に対してカルシヤ組成物とアルカリ組成物からなるアルカリ形硬化剤を20質量部以上加えて水系組成物と共に変形性混和物を調製して耐水・耐熱性固化体が提供される技術が開示されている。  Further, in the prior application (Japanese Patent Laid-Open No. 12-263661) by the present inventors, a wet fluid obtained by dispersing a silica-alkali composition having a silanol group and an aluminate composition of an alkaline earth metal in water is used. Non-form hydraulic silica-based binders are disclosed. Furthermore, in the prior application technique by the present inventors (Japanese Patent Laid-Open No. 2002-128550), 20 parts by mass or more of an alkali-type curing agent composed of a calcium composition and an alkali composition is added to 100 parts by mass of a silicate material. A technique is disclosed in which a deformable admixture is prepared together with an aqueous composition to provide a water / heat resistant solidified product.

さらに、先願技術(特開2002−249348)には、硫黄のオキシ酸塩組成物、アルカリ組成物、カルシヤ組成物、水系組成物の4者のシラノール基含有化合物を主軸とする組成物で構成される常温水硬性固化材が開示されている。また、先願技術(特開2003−013061)には、カルシヤ組成物と硫酸アルミ組成物とリン酸アルミ組成物で構成される粉末状ワンパック品の無害化改質処理剤が開示されている。また、先願技術(特開2003−122953)には、熱履歴を受けて酸化硫黄含有する火山灰にカルシヤ等を添加配合して予め800℃以下で熱処理したカルシヤ−シリカ組成物を一旦調製しているが、品質保持性を確保するに充分な不活性化処理がなされていないカルシヤ−シリカ組成物に水酸化ナトリウムを加えてシラノール基を有する活性ケイ酸塩を一構成成分とする水硬性固化材の製造法が開示されている。  Furthermore, the prior application technique (Japanese Patent Application Laid-Open No. 2002-249348) is composed of a composition mainly composed of four silanol group-containing compounds: a sulfur oxyacid salt composition, an alkali composition, a calcium composition, and an aqueous composition. A room temperature hydraulic solidified material is disclosed. In addition, the prior application technique (Japanese Patent Laid-Open No. 2003-013061) discloses a detoxifying treatment agent for a powdery one-pack product composed of a calcium composition, an aluminum sulfate composition, and an aluminum phosphate composition. . In addition, in the prior application technique (Japanese Patent Application Laid-Open No. 2003-122953), a calci-silica composition that has been heat-treated at a temperature of 800 ° C. or lower in advance by adding calcia and the like to volcanic ash containing sulfur oxide in response to a thermal history is prepared. Hydraulic solidifying material comprising activated silicate having silanol group as a constituent component by adding sodium hydroxide to calcium-silica composition which has not been sufficiently inactivated to ensure quality retention The manufacturing method is disclosed.

また、先願技術(特開2004−050158)には、重金属類の固定化材としてシラノール基を有する活性シリカ、反応性アルミナ、水酸化ナトリウムおよびカルシヤ組成物の4者で構成される粉末状ワンパックの複合成分が開示されているが、製品の品質保持性に配慮した特別な手段ならびに工夫は開示されていない。また、先願技術(特開2005−097069)には、混合原料を820℃以上で調製される不活性なシリケートに対して、ナトリウムとシラノール基を保有するアクティブシリカ、必要に応じてサルファメントを加えた基本3成分の基礎成分、さらに基礎成分に補足成分を加えた4成分の複合成分で構成され、水系溶媒を介した反応により、形状化(固化・結着化・注充填等)ならびに無害化(pH10未満、固定化・分解等)処理機能を190℃以下、常温でも発揮する粉粒体組成物で、棚寿命が確保されているシラノール基含有硬化材料からなる改質処理剤技術が開示されている。  In addition, in the prior application technique (Japanese Patent Application Laid-Open No. 2004-050158), a powdery one composed of active silica having a silanol group, reactive alumina, sodium hydroxide and a calcium composition as an immobilizing material for heavy metals. Although the composite component of the pack is disclosed, no special means or device in consideration of the product quality retention is disclosed. In addition, in the prior application technique (Japanese Patent Application Laid-Open No. 2005-097069), an active silica having sodium and silanol groups is added to the inert silicate prepared as a mixed raw material at 820 ° C. or higher, and sulfament is provided if necessary. Consists of 3 basic components added and 4 composite components with supplemental components added to the basic components. Shaped (solidified, bound, poured, etc.) and harmless by reaction via aqueous solvent Disclosed is a modified processing agent technology consisting of a silanol group-containing cured material that has a shelf-life ensured with a granular composition that exhibits a processing function (below pH 10, immobilization / decomposition, etc.) at a temperature of 190 ° C. or less at room temperature Has been.

しかるに、これら従来技術において、少なくとも常温における改質処理操作により、カルシヤ含有成分、ナトリウム含有成分ならびに硫黄含有成分の3者で構成されるpH値で12以上の強いアルカリ性を示す改質処理剤により、熱履歴を受けているシリケートからなる廃棄物類を構成する休眠成分のケイ酸塩化合物を予め活性化せしめて活用して、系内に有害物資として共存するアルカリ成分ならびに有害元素群をpH10未満で水不溶性鉱物として固定化せしめる技術、しかも有害物資を固定化形成せしめた水不溶性鉱物である処理物が、中性域にある水系溶媒のみならず、酸性雨が想定される酸性域にあるpH4の溶液にさらしても、処理物に固定化されたアルカリ成分ならびに有害元素群を系外に溶出させない処理条件ならびに処理技術に係る技術開示はない。  However, in these conventional techniques, at least by a modification treatment operation at normal temperature, a modification treatment agent exhibiting strong alkalinity of 12 or more at a pH value constituted by three components of a calcium-containing component, a sodium-containing component and a sulfur-containing component, Activated and utilized the dormant component silicate compound that constitutes the waste consisting of silicates that have undergone a thermal history, the alkaline component and harmful element group coexisting as harmful substances in the system at a pH of less than 10 The technology to fix as water-insoluble minerals, and the water-insoluble minerals that have fixed and formed harmful substances are not only water-based solvents in the neutral range but also pH 4 in the acidic range where acid rain is expected. Treatment conditions and treatments that do not elute alkaline components and harmful elements immobilized on the treated material out of the system even when exposed to the solution Technology disclosure is not related to the surgery.

さらにまた、従来技術におけるダイオキシン類の無害化処理技術としては、一般には800℃以上の高温で熱処理してダイオキシン類を分解する無害化技術が採択されている。その他ダイオキシン類を無害化せしめる技術として、▲1▼金属ナトリウムによる還元分解方法、▲2▼水酸化マグネシウムを吸着剤とする処理方法、▲3▼光触媒シリカゲルによる処理方法、▲4▼活性炭を吸着剤とする処理方法等が開示されている。  Furthermore, as a detoxification treatment technique for dioxins in the prior art, a detoxification technique for decomposing dioxins by heat treatment at a high temperature of 800 ° C. or higher is generally adopted. Other techniques for detoxifying dioxins include: (1) reductive decomposition with metallic sodium, (2) treatment with magnesium hydroxide as adsorbent, (3) treatment with photocatalytic silica gel, and (4) activated carbon as adsorbent. And the like are disclosed.

しかるに、100℃以下の低温でダイオキシン類を効率よく分解して無害化処理する技術の開示はない。しかも、従来技術においては、重金属類ならびにダイオキシン類が併存している無機質系廃棄物類等を改質対象素材として、水を介してpH12以上を示す3者で構成される改質処理剤を加えて、少なくとも常温において、複数の共存有害元素群を同時に単一薬剤(改質処理剤)の配合により、全ての有害元素群をpH値が10未満で固定・水不溶化する共に、同時に少なくとも常温において、共存するダイオキシン類を分解処理して無害化せしめる処理技術の開示はなされていない。  However, there is no disclosure of a technique for efficiently decomposing and detoxifying dioxins at a low temperature of 100 ° C. or lower. In addition, in the prior art, a modification treatment agent composed of three members having a pH of 12 or more is added via water, using inorganic wastes and the like in which heavy metals and dioxins coexist as materials to be modified. In addition, at least at room temperature, by co-mixing multiple coexisting harmful element groups with a single agent (modifying agent) at the same time, all the harmful element groups are fixed and insoluble in water at a pH value of less than 10, and at the same time at least at room temperature. However, there is no disclosure of a processing technique for decomposing and detoxifying coexisting dioxins.

本発明おける課題は、熱履歴シリケートであり、大量に発生して処理・処分に窮してきた廃棄物類から溶出する有害物質が、生活環境を汚染して人や動植物に悪影響を及ぼしてきた実態に対処できる技術にあり、廃棄物類を構成する熱履歴シリケートに共存する有害物質類を環境に対し低負荷型で、エネルギー消費が省エネ型で、処理工程が低コスト型で改質処理が実行できる処理技術にある。しかも廃棄物類が改質処理されて再生利用可能な結着形状体として提供されるには、改質処理した結着形状体が広い用途分野のニーズに応える諸物性を確保している必要があり、低価格で安全に供給される有効な結着形状体でなくては循環型社会の構築は実質的に不可能であるところに課題がある。  The subject in the present invention is a heat history silicate, and the actual condition that harmful substances eluted from wastes that have been generated and treated and disposed of in large quantities have contaminated the living environment and have adversely affected humans, animals and plants. Is a technology that can cope with the toxic substances that coexist in the heat history silicate that constitutes the waste, is low environmental load type, energy consumption is energy saving type, processing process is low cost type, reforming process is executed It is in processing technology that can. In addition, in order for waste to be reformed and provided as a reusable binding shape body, it is necessary that the modified binding shape body has various physical properties to meet the needs of a wide range of application fields. There is a problem in that it is practically impossible to build a recycling society without an effective binding shape that can be safely supplied at a low price.

従来技術において、ケイ酸塩系の廃棄物類を処理・処分して、特に廃棄物類が共存する有害物質である有害重金属類、またフッ素やホウ素を少なくとも常温で無害化処理しようとする場合、処理対象の廃棄物類に対して系外外部から複数の薬剤や改質処理剤、またバインダーや固化材等を導入して、キレート化処理、中和・水酸化物形成処理、被覆・固化処理等により有害物質に対する不溶化処理が施されてきた。  In the prior art, when processing and disposing of silicate wastes, especially when trying to detoxify harmful heavy metals, which are harmful substances with which wastes coexist, and fluorine and boron at least at room temperature, Introducing multiple chemicals, modifying agents, binders and solidifying materials from outside the system to the waste to be treated, chelating treatment, neutralization / hydroxide formation treatment, coating / solidification treatment The insolubilization process with respect to a toxic substance has been performed by the above.

例えば、本発明者等の先願技術(特開2002−128550)においては改質対象素材100質量部に対して、アルカリ系硬化剤からなるアリカリ性成分を20質量部以上の多量を添加して処理する技術が開示されている。しかるに、この先願技術においては、重金属類を不溶化対象元素とする不溶化技術は開示されているが、強いアルカリに充分可溶な酸類元素群であるホウ素やフッ素を同時に不溶化せしめる技術開示はない。しかるに一方、廃棄物類を構成するケイ酸塩化合物を活性化して活用するには、pH12以上の高いアルカリ性からなる活性化機能を有する改質処理剤が必要である。  For example, in the prior application technique of the present inventors (Japanese Patent Laid-Open No. 2002-128550), a large amount of 20 parts by mass or more of an antarian component made of an alkaline curing agent is added to 100 parts by mass of the material to be modified. Techniques for processing are disclosed. However, in this prior application technique, an insolubilization technique using heavy metals as elements to be insolubilized is disclosed, but there is no technical disclosure that simultaneously insolubilizes boron and fluorine, which are acid elements sufficiently soluble in strong alkali. On the other hand, in order to activate and utilize the silicate compound constituting the wastes, a modifying agent having an activation function consisting of a high alkalinity of pH 12 or higher is required.

本発明の第一課題は、本発明の改質対象素材である廃棄物類等から溶出するカドミニウム、砒素、水銀、鉛、クロム、セレン、ホウ素、フッ素等からなる有害元素群を一括して取り込み水不溶性鉱物を形成せしめた必須成分のシリカならびにアルミナ成分を廃棄物類の構成成分である休眠成分に求め、遊離のイオン性ナトリウムによるpH12以上の高いアルカリ濃度により活性化を行い、次いで形成される水不溶性鉱物に有害元素群を取り込む時には、有害元素群の水不溶性鉱物への取り込みを阻害しない範囲での低いアルカリ濃度が管理されているカルシヤ含有成分、ナトリウム含有成分および硫黄含有成分の3者で構成される改質処理剤を採択する処理技術にある。  The first object of the present invention is to collect a group of harmful elements consisting of cadmium, arsenic, mercury, lead, chromium, selenium, boron, fluorine, etc., which are eluted from the wastes that are the materials subject to modification of the present invention. The silica and alumina components, which are essential components that have formed water-insoluble minerals, are obtained as dormant components that are constituents of wastes, activated by a high alkali concentration of pH 12 or higher with free ionic sodium, and then formed. When incorporating a harmful element group into a water-insoluble mineral, a calcium-containing component, a sodium-containing component, and a sulfur-containing component whose low alkali concentration is controlled within a range that does not inhibit the incorporation of the harmful element group into the water-insoluble mineral. The processing technology adopts a modified processing agent.

しかも、ここに形成された有害元素群を取り込んだ水不溶性鉱物は、環境に二次公害を起こさないpH値で10未満が確保されており、中性域のみならず酸性雨が想定されるpH4の酸性域に暴露されたときにも、有害元素群ならびにアルカリ成分を水溶出せしめない不溶化処理が施されていることが重要であり、この現象により処理物が自然界で長期的に安全に不溶化現象の確保・維持が可能となり、有害元素類共存の廃棄物類を耐水性でpH値が10未満の結着形状体として有効活用することが可能おとなる。  In addition, the water-insoluble minerals incorporating the harmful element group formed here have a pH value of less than 10 that does not cause secondary pollution in the environment, and pH 4 where acid rain is assumed as well as the neutral range. It is important that insoluble treatments that do not allow water to elute toxic elements and alkali components are applied even when exposed to acidic areas, and this phenomenon makes the treated products safe and insoluble in nature for a long time. Can be ensured and maintained, and wastes coexisting with harmful elements can be effectively utilized as a bound shape body having water resistance and a pH value of less than 10.

さらに、本発明の第一課題において、改質対象素材である廃棄物類から溶出する有害元素類に止まらず、多くに廃棄物類に共存する有害なダイオキシン類に対して、少なくとも常温において、粉粒体廃棄物類の休眠成分を活性化活用して改質処理することにより、有害元素類の不溶化処理と共に、ダイオキシン類も少なくとも常温において分解せしめて無害化処理が施され、有害元素類と共にダイオキシン類共存の廃棄物類を少なくとも存在する原位置で改質対象素材を改質処理して、各分野で有効活用できる耐水性の結着形状体に改質する処理技術にある。  Furthermore, in the first problem of the present invention, not only harmful elements that are eluted from the waste that is the material to be modified, but also harmful dioxins that often coexist in the waste, at least at room temperature, By activating and utilizing the dormant component of granular wastes, insoluble treatment of harmful elements, dioxins are also decomposed at least at room temperature and detoxified, and together with harmful elements, dioxin This is a processing technology for reforming a material to be reformed at the position where at least existing coexisting wastes are present, and reforming it into a water-resistant binding shape that can be effectively used in each field.

本発明の第二課題は、熱履歴ケイ酸塩化合物を主成分とする廃棄物類等を改質対象素材として、廃棄物類のシリカ、アルミナ、カルシヤ等の不活性な休眠成分に対してpH値が12以上の改質処理剤を採択し、水を介して3者を混和し、少なくとも常温において改質対象素材が保有する不活性な休眠成分を活性化すること、ついで活性化された成分類を活用して粉粒体改質対象素材を結着・硬化せしめて耐水性で再泥化することなくpH値が10未満で一定強度が確保され結着形状体に改質処理する処理技術にある。  The second problem of the present invention is that wastes and the like mainly composed of a heat history silicate compound are used as a material to be modified, and the pH of an inert dormant component such as silica, alumina, and calcium in wastes. Adopting a modification treatment agent with a value of 12 or more, mixing the three through water, activating the inactive dormant component possessed by the material to be modified at least at room temperature, and then activating the activated component Processing technology that uses the classification to bind and harden the material to be modified with granular material, and is water resistant and re-mudged, ensuring a constant strength with a pH value of less than 10 and modifying the material into a bonded shape. It is in.

したがって、本発明における課題は、第一ならびに第二の課題を同時に低コストで環境に低負荷型で安全に解消するために、少なくとも常温における省エネ型の改質処理工程を可能とする処理設備を採択して、カルシヤ含有成分と酸化ナトルウム含有成分と硫黄含有成分と3者を特定配合に管理してpH12を超える活性化活用成分を予め調製して、該活性化活用成分を熱履歴シリケートである廃棄物類を改質対象素材として活用する一連の作業工程に付することにより、廃棄物類を再生利用可能なpH値10未満の結着形状体に改質処理せしめて、処理・処分に窮してきた廃棄物類を安価に再資源化資材として各分野に提供して環境問題における課題を解消することにある。  Therefore, the object of the present invention is to provide a processing facility that enables an energy-saving reforming process step at least at room temperature in order to solve the first and second problems simultaneously at a low cost and in a low-load environment. Adopted and prepared in advance a component containing calcium, a component containing sodium oxide, a component containing sulfur, and an activated component exceeding pH 12 by managing them in a specific formulation, and the activated component is a heat history silicate. By subjecting wastes to a series of work processes that utilize them as materials to be reformed, wastes can be reformed into binder-shaped bodies with a pH value of less than 10 for recycling and disposal. The purpose of this is to provide the various wastes as recyclable materials at low cost to each field to solve the problems in environmental problems.

本発明によれば、熱履歴シリケートを改質対象素材として、少なくとも常温で水系溶媒を介して活性化し、無害化処理および形状化処理を施す改質処理機能を発揮して無公害型の結着形状体に改質処理する機能を有する改質処理剤において;  According to the present invention, a heat history silicate is used as a material to be modified, activated at least at room temperature via an aqueous solvent, and exhibits a modification treatment function that performs a detoxification treatment and a shaping treatment, and is a pollution-free binding. In a modifying agent having a function of modifying the shape body;

上記の熱履歴シリケートが、乾燥物の酸化物基準で表してシリカ成分を20ないしは80質量%、アルミナ成分を5ないしは35質量%、およびカルシヤ成分を1ないしは40質量%を含有して熱履歴を受けている不活性な休眠成分のケイ酸塩系化合物で構成される人工合成品、ゴミ・廃棄物・汚泥の焼却灰、窯業関連廃材・資材もしくは火山噴出物からなる粉粒体であり;  The above-mentioned heat history silicate contains 20 to 80% by mass of silica component, 5 to 35% by mass of alumina component, and 1 to 40% by mass of calcium component, expressed on the basis of oxide of the dried product. Artificial synthetic products composed of inactive dormant silicate compounds, incineration ash of waste, waste, sludge, ceramics-related waste materials / materials or powders of volcanic products;

上記水系溶媒が、自然水、人工処理水、排水類ないしは包含水の群より選ばれる単独ないし2種以上の組み合わせの水系液体であり;  The aqueous solvent is a single or a combination of two or more aqueous liquids selected from the group of natural water, artificially treated water, wastewater or inclusion water;

上記の改質処理剤が、乾燥物における有効成分換算で表してカルシヤ含有成分に含まれるカルシヤ100質量部に対して、ナトリウム含有成分に含まれる酸化ナトリウムを0.1ないしは5質量部ならびに硫黄含有成分に含まれる硫黄を酸化物換算で1ないしは50質量部の酸化物基準で表した配合割合で3者成分がワンパック粉粒体を構成しており、該ワンパック粉粒体の水サスペンジョンpHが12を超えるアルカリ性である改質処理剤が提供される。  The above-mentioned modifying treatment agent is 0.1 to 5 parts by mass of sodium oxide contained in the sodium-containing component and sulfur-containing with respect to 100 parts by mass of the calcium contained in the calcium-containing component expressed in terms of active ingredients in the dried product. The three-component component constitutes a one-pack powder at a blending ratio in which sulfur contained in the component is expressed in terms of oxide in terms of oxide of 1 to 50 parts by mass, and the water suspension pH of the one-pack powder A modification treatment agent is provided which has an alkalinity greater than 12.

人工合成品
本発明によれば、前記の熱履歴シリケートである人工合成品の粉粒体が、ケイ酸塩組成物、カルシヤ組成物ならびにアルミナ組成物の群より選ばれる単独ないし2種以上の組み合わせの混合原料で予め調製されており、該混合原料が主成分として乾燥物の酸化物基準で表してシリカ100質量部に対して、カルシヤ30ないし350質量部ならびにアルミナを10ないし150質量部、必要に応じて酸化ナトリウムを1ないし50質量部の範囲で構成されており、該混合原料を820ないし1500℃の範囲で少なくとも15分間熱処理し、次いで回収された熱処理物を80メッシュ、好むらくは150メッシュ篩通過の微粒子に粉砕・分級して調製されている改質処理剤が提供される。
Artificial Synthetic Product According to the present invention, the above-mentioned heat-histosilicate silicate artificial granule is selected from the group consisting of a silicate composition, a calcium composition and an alumina composition. 30 to 350 parts by weight of calcium and 10 to 150 parts by weight of alumina are required for 100 parts by weight of silica expressed as oxides of the dried product as a main component. The mixed raw material is heat-treated at a temperature of 820-1500 ° C. for at least 15 minutes, and the recovered heat-treated product is 80 mesh, preferably 150. A modifying agent prepared by pulverizing and classifying fine particles passing through a mesh sieve is provided.

含水体
本発明によれば、前記の熱履歴シリケートである人工合成品、ゴミ・廃棄物・汚泥の焼却灰、窯業関連廃材・資材もしくは火山噴出物からなる粉粒体を乾燥物基準で100質量部に対して水が140質量部以下の量割合で包含担持されている粉粒体の含水体、ないしはヘドロ・底質・汚泥処理ケーキの含水泥土もしくは湿潤状態にある粘土・土壌類の土質土で固形分100質量部に対して水が140質量部以下の量割合で包含している含水体である改質処理剤が提供される。
Hydrous material According to the present invention, the above-mentioned heat history silicate is an artificial synthetic product, dust, waste, sludge incineration ash, ceramic industry-related waste materials / materials or volcanic products 100 mass on a dry matter basis The water content of the granular material in which water is included and supported at a ratio of 140 parts by mass or less relative to the part, or the water content of sludge, bottom sediment, sludge treated cake, or clay and soil soils in a wet state Thus, there is provided a modifying agent which is a hydrous material containing water in an amount ratio of 140 parts by mass or less with respect to 100 parts by mass of the solid content.

有害化学物質
本発明によれば、上記の熱履歴シリケートが、原位置または持込位置に存在して、土壌汚染の環境基準項目で示されるカドミニウム、砒素、水銀、鉛、クロム、セレン、ホウ素ないしはフッ素の群より選ばれる単独ないし2種以上の組み合わせの水溶出有害元素群、アルカリ金属元素群、窒素の化合物類ないしはダイオキシン類の単独ないし2種以上の組み合わせの有害化学物質が環境基準を超える範囲で共存している粉粒体ないしは含水体である改質処理剤が提供される。
Hazardous chemical substance According to the present invention, the above-mentioned heat history silicate is present in the original position or in the carry-in position, and cadmium, arsenic, mercury, lead, chromium, selenium, boron or Scope of exceeding one or more combinations of water-extracting harmful element group, alkali metal element group, nitrogen compounds or dioxins, or two or more combinations of harmful chemical substances selected from the group of fluorine. The modifying agent which is a granular material or a hydrated body coexisting with is provided.

自然水、人工処理水、排水類ないしは包含水
本発明によれば、前記の水系溶媒が、雨水、河川・湖沼水・たまり水、湧き水、井戸水、海水、人工池・ダム水である自然水;飲料水、工場用水、農業用水、水道水、下水道処理水、産業界の副生水である人工処理水;産業界の排水、生活排水、各種の処理水である排水類;含水土質、底質、土壌地盤、産業廃棄物類、改質対象素材、改質処理剤の包含水の群より選ばれる単独ないし2種以上の組み合わせ水系液体である改質処理剤が提供される。
Natural water, artificially treated water, wastewater or inclusion water According to the present invention, the water-based solvent is rainwater, river, lake water, pool water, spring water, well water, seawater, artificial pond / dam water; Drinking water, factory water, agricultural water, tap water, sewage treated water, artificial treated water that is by-product water of industry; industrial wastewater, domestic wastewater, wastewater that is various treated water; hydrous soil, sediment There is provided a reforming agent that is a single or a combination of two or more aqueous liquids selected from the group consisting of soil ground, industrial wastes, materials to be reformed, and water included in the modifying agent.

本発明によれば、前記改質処理剤を構成するカルシヤ含有成分が、酸化物基準で表して有効成分であるカルシヤを少なくとも25質量%含有しているカルシヤ含有の化合物ないしは組成物からなる粉粒体である改質処理剤が提供される。  According to the present invention, the granule comprising a calcium-containing compound or composition in which the calcium-containing component constituting the modifying treatment agent contains at least 25% by mass of an active ingredient calcium expressed on an oxide basis. A body modification agent is provided.

本発明によれば、前記改質処理剤を構成するカルシヤ含有成分が、処理石灰を包含する焼却灰類、高炉・製鋼スラグ類、ケイカル廃材、セメント類、ないし廃棄・副生石こうないしはカルシウム塩化合物類の群より選ばれる単独ないし2種以上の組み合わせの休眠成分からなる熱履歴シリケートに共存して有効成分であるカルシウム成分を酸化物基準で表して少なくとも20質量%の量で確保されている含カルシウム休眠成分であり、このとき併配合されるナトリウム含有成分が、活性な水酸化ナトリウムの組み合わせからなる粉粒体ないしは含水体である改質処理剤が提供される。  According to the present invention, the calcium-containing component constituting the modifying treatment agent is incinerated ash containing treated lime, blast furnace / steel slag, calcium waste, cement, or waste / byproduct gypsum or calcium salt compound The calcium component which is an active ingredient coexisting with the heat history silicate which consists of a dormant ingredient of single or 2 or more types of combinations chosen from the kind group is secured in the amount of at least 20 mass% expressed on the oxide basis. There is provided a modifying agent, which is a calcium dormant component, wherein the sodium-containing component that is co-mixed at this time is a powder or a hydrated body comprising a combination of active sodium hydroxide.

本発明によれば、前記改質処理剤を構成するナトリウム含有成分が、酸化物基準で表して有効成分である酸化ナトリウムを少なくとも2質量%含有しているナトリウム含有の化合物ないしは組成物からなる粉粒体である改質処理剤が提供される。  According to the present invention, a powder comprising a sodium-containing compound or composition in which the sodium-containing component constituting the modifying treatment agent contains at least 2% by mass of sodium oxide as an active ingredient expressed on an oxide basis. A modification treatment agent that is a granule is provided.

本発明によれば、前記改質処理剤を構成するナトリウム含有成分が、下記組成式(1)

Figure 2006247645
[式中:Mはナトリウムないしカリウム元素、aは0.1ないし4の数、wは16ないし50の数]で表されるケイ酸アルカリの群より選ばれる単独ないし2種以上の組み合わせの液状ケイ酸アルカリからなる含水体である改質処理剤が提供される。According to the present invention, the sodium-containing component constituting the modifying treatment agent has the following composition formula (1):
Figure 2006247645
[Wherein, M is an element of sodium or potassium, a is a number of 0.1 to 4, and w is a number of 16 to 50] alone or in combination of two or more kinds selected from the group of alkali silicates There is provided a modifying agent which is a water-containing body composed of an alkali silicate.

本発明によれば、前記改質処理剤を構成するナトリウム含有成分が、ゴミ焼却灰、汚泥焼却灰、赤泥ないしは芒硝類廃液の回収物の群より選ばれる単独ないし2種以上の組み合わせの休眠成分からなる熱履歴シリケートに共存して有効成分であるナトリウム成分を酸化物基準で表して少なくとも1.5質量%含有する含ナトリウム休眠成分であり、このとき併配合されるカルシヤ含有成分が、活性な酸化カルシウムないし水酸化カルシウムの組み合わせからなる粉粒体ないし含水体である改質処理剤が提供される。  According to the present invention, the sodium-containing component constituting the modifying treatment agent is a dormancy of one or a combination of two or more selected from the group of waste incineration ash, sludge incineration ash, red mud or salted glass waste liquid collection It is a sodium-containing dormant component containing at least 1.5% by mass of the sodium component as an active ingredient coexisting with the heat history silicate consisting of the components. There is provided a modifying agent which is a powder or a hydrated body comprising a combination of calcium oxide or calcium hydroxide.

本発明によれば、前記改質処理剤を構成する硫黄含有成分が、無水物の硫黄分基準で表して有効成分である硫黄分を少なくとも18質量%含有している硫黄のオキシ酸化合物ないし硫化物からなる粉粒体である改質処理剤が提供される。  According to the present invention, the sulfur-containing component that constitutes the modifying treatment agent is a sulfur oxyacid compound or sulfide containing at least 18% by mass of the sulfur component that is an active component expressed on the basis of the sulfur content of the anhydride. There is provided a modifying agent that is a granular material made of a product.

本発明によれば、前記の改質処理剤を活用して、必要に応じて機能付与剤を付加して少なくとも常温で水系溶媒を介して、改質対象素材となる休眠成分からなる熱履歴シリケートに加えて活性化混和物とする混和工程、必要に応じて該活性化混和物を形状化処理物とする加工工程、次いで該活性化混和物ないし該形状化処理物を所定雰囲気中に開放せしめて結着形状体とする養生工程で構成される一連の作業工程からなる改質処理方法において;  According to the present invention, a heat history silicate composed of a dormant component as a material to be modified is added through a water-based solvent at least at room temperature by adding a function-imparting agent as necessary using the above-described modification treatment agent. In addition to the mixing step of making the activated admixture, if necessary, the processing step of making the activated admixture a shaped product, and then releasing the activated admixture or the shaped product into a predetermined atmosphere. In a reforming method comprising a series of work steps composed of a curing step to form a binding shape;

上記の機能付与剤が、サプリメント、インプルーブメント、ファンクションメントもしくはレインホースメントの単独ないし2種以上の組み合わせの粒径500μ以下の粉粒体で構成されており;  The above-mentioned function-imparting agent is composed of a powder, having a particle size of 500 μm or less, which is a supplement, improvement, functionment or rain reinforcement alone or in combination of two or more thereof;

上記の混和工程が、原位置または持込位置に存在する熱履歴シリケートを乾燥物基準で100質量部に対して、改質処理剤を乾燥物基準で2ないし20質量部未満を加え、必要に応じて機能付与剤を400質量部以下の量で付加して混和して活性化混和物とし、該活性化混和物中の含有水分の含水率が10ないし70質量%範囲に確保される状態になるように必要に応じて水系溶媒を加えて量割合を調整して混和し、該活性化混和物が常温にて混和・放置される3時間の間のpH値が12を超える状態が確保されてバサバサ状、可塑状、マヨネーズ状、糊状ないしはスラリー状に調製される工程であり;  The above mixing step is performed by adding 2 to less than 20 parts by mass of the modification treatment agent with respect to 100 parts by mass of the heat history silicate present in the original position or the carry-in position on the basis of dry substance. Accordingly, a function-imparting agent is added and mixed in an amount of 400 parts by mass or less to make an activated admixture, and the moisture content of the water content in the activated admixture is ensured in the range of 10 to 70 mass%. As necessary, an aqueous solvent is added and the amount is adjusted and mixed to ensure that the activated admixture is mixed and allowed to stand at room temperature for a pH value exceeding 12 for 3 hours. A process that is prepared in the form of rust, plastic, mayonnaise, paste or slurry;

上記の加工工程が、必要に応じて該活性化混和物を原位置非成型物、耐水性粉粒体物ないしは形状加工成型物からなる形状化処理物とする工程であり;  The above-mentioned processing step is a step of making the activated admixture a shaped processed product made of an in-situ non-molded product, a water-resistant granular material or a shaped processed molded product, if necessary;

上記の養生工程が、該活性化混和物ないしは該形状化処理物を常温から100℃範囲にある常圧、加圧、減圧条件下における気中、水中、海中、土中、溶液中、蒸気中、非酸素ガス中の雰囲気の群より選ばれる単独雰囲気中ないし2種以上の組み合わせの多段雰囲気中に少なくとも15分間解放して反応・養生を進行せしめて結着硬化の完了している自己完結型の原位置非成型品、耐水性粉粒体品ないしは形状加工成型品からなる結着形状体とする工程であり;  In the curing process described above, the activated admixture or the shaped product is subjected to normal pressure, pressurization, and decompression under normal pressure, pressurization, and decompression conditions in air, water, sea, soil, solution, and steam. A self-contained type in which the binding and curing are completed by allowing the reaction and curing to proceed for at least 15 minutes in a single atmosphere selected from the group of non-oxygen gas atmospheres or in a multistage atmosphere of a combination of two or more. In-situ non-molded product, water-resistant granular product or shape-processed molded product to form a bound shape;

上記の改質処理方法が、熱履歴シリケートを改質対象素材として、上記の一連の作業工程に付して調製される活性化混和物のアルカリ性成分を固定化してpH10未満が確保され、該改質対象素材に有害物質が共存するときは該有害物質を固定・不溶化する無害化処理を施し、同時に粉粒体熱履歴シリケートを耐水性で水中再泥化しない形状化処理を施して自己完結型の結着形状体に改質処理する改質処理方法が提供される。  The above reforming treatment method fixes the alkaline component of the activated admixture prepared by applying the heat history silicate as a material to be modified to the above-described series of work steps to secure a pH of less than 10, When harmful substances coexist in the target material, the detoxification treatment to fix and insolubilize the harmful substances is performed, and at the same time, the granule thermal history silicate is water-resistant and shaped to prevent re-mudging in water. There is provided a modification treatment method for modifying the binding shape of the present invention.

本発明によれば、前記機能付与剤であるサプリメントが、アルカリ金属塩ないしアルカリ土類金属塩の化合物を主成分とするアルカリ補充組成物、硫黄のオキシ酸化合物ないしは硫化物を主成分とする硫黄含有組成物、2価ないし3価の鉄化合物である鉄塩補充組成物、親油性で活性なフェロケイ酸塩組成物もしくはシラノール基含有組成物であるケイ酸塩補充組成物の群より選ばれる単独ないし2種以上の組み合わせの改質処理剤を補充する化合物ないしは組成物からなる粉粒体である改質処理方法が提供される。  According to the present invention, the supplement as the function-imparting agent is an alkali replenishing composition mainly comprising a compound of an alkali metal salt or alkaline earth metal salt, sulfur oxyacid compound or sulfur mainly comprising a sulfide. A single composition selected from the group consisting of an iron salt supplement composition that is a divalent to trivalent iron compound, a lipophilic and active ferrosilicate composition, or a silicate supplement composition that is a silanol group-containing composition. There is also provided a modification treatment method which is a powder or a granule comprising a compound or composition supplemented with a combination of two or more kinds of modification treatment agents.

本発明によれば、前記の機能付与剤であるインプルーブメントが、改質処理機能を改善するリン酸根組成物、改質処理時の作業性を改善するバリウム塩組成物もしくは改質処理作用を向上せしめる分散媒質組成物の群より選ばれる単独ないし2種以上の組み合わせの改質処理剤が有する改質処理の機能性ないしは作業性を改善する化合物ないしは組成物からなる粉粒体である改質処理方法が提供される。  According to the present invention, the improvement as the function-imparting agent improves the phosphate radical composition that improves the modification treatment function, the barium salt composition that improves the workability during the modification treatment, or the modification treatment action. A reforming treatment which is a powder or a granular material composed of a compound or composition which improves the functionality or workability of the reforming treatment possessed by one or a combination of two or more modifying treatment agents selected from the group of disperse dispersion medium compositions A method is provided.

本発明によれば、前記の機能付与剤であるファンクションメントが、形成される水不溶性鉱物を成長させる結晶タネ組成物、結着形状体に緩衝性を付与する緩衝帯形成組成物、各種の機能性液状素材を担持する担持吸着組成物、熱に耐える耐熱火組成物、熱遮断性ないしは保温性を発揮する断熱・保温組成物、固−液分離を促進する沈殿凝集組成物もしくは各種の機能性を付与する機能付与組成物の群より選ばれる単独ないし2種以上の組み合わせの改質処理される結着形状体の物性もしくは機能性を改良・改善する化合物ないしは組成物からなる粉粒体である改質処理方法が提供される。  According to the present invention, the function as the function-imparting agent is a crystal seed composition for growing a water-insoluble mineral to be formed, a buffer zone-forming composition for imparting buffering properties to a bound shape, and various functions. Supported adsorbent composition carrying a heat-resistant liquid material, heat-resistant fire-resistant composition resistant to heat, heat insulation / heat-retaining composition exhibiting heat-blocking or heat-retaining properties, precipitation aggregation composition promoting various solid-liquid separations, or various functionalities A compound or composition comprising a compound or composition that improves or improves the physical properties or functionality of a binder-shaped body that is subjected to a modification treatment of a single or a combination of two or more selected from the group of function-providing compositions A reforming method is provided.

本発明によれば、前記の機能付与剤であるレインホースメントが、結着形状体を補強・補足する繊維質組成物、同様に細骨材ないしは粗骨材の群より選ばれる単独ないし2種以上の組み合わせの補強性材料である改質処理方法が提供される。  According to the present invention, the rain reinforcement as the function-imparting agent is a fiber composition that reinforces and supplements the bound-shaped body, as well as single or two kinds selected from the group of fine aggregates or coarse aggregates. There is provided a reforming method which is a reinforcing material of the above combination.

本発明によれば、前記の原位置非成型品が、原位置に持ち込んで施設された処理装置により、原位置に存在して有害物質を共存する汚染土壌地盤の乾燥物基準で100質量部に対して、改質処理剤を5ないし30質量部、汚必要に応じて機能付与剤を400質量部以下の量で加え、さらに染土壌地盤が保有している水分を勘案して水系溶媒を少なくとも20質量部以上になる量で混和して活性化混和物を原位置で調整され、  According to the present invention, the in-situ non-molded product is brought into the in-situ position to 100 parts by mass based on the dry matter of the contaminated soil ground existing in the in-situ and coexisting with harmful substances. On the other hand, 5 to 30 parts by mass of the modifying agent, and 400% by mass or less of the function-imparting agent as required for soiling, and at least an aqueous solvent in consideration of the water content of the dyed soil ground. The activated admixture is adjusted in situ by mixing in an amount of 20 parts by mass or more,

次いで原位置で調製された活性化混和物に対して加工工程を経ることなく原位置における環境下の常温雰囲気中に少なくとも24時間曝露養生することにより土壌地盤、軟弱地盤、道路、堤ないしは農地・宅地・公共用地に無害化処理および形状化処理が施されている結着形状体である改質処理方法が提供される。  The activated admixture prepared in-situ is then subjected to at least 24 hours of exposure and curing in an ambient ambient temperature in the in-situ environment without undergoing any processing steps, thereby allowing soil soil, soft ground, roads, dikes or farmland / There is provided a modification treatment method which is a bound shape body in which detoxification treatment and shaping treatment are performed on residential land and public land.

本発明によれば、前記の形状加工成型品が、原位置に持ち込んで施設された処理装置により、原位置に存在して有害物質を共存する汚染土壌地盤、汚染軟弱地盤、汚染道路・堤ないしは汚染農地・宅地・公共用地の乾燥物基準で100質量部に対して、改質処理剤を5ないし30質量部、必要に応じて機能付与剤を400質量部以下の量で加え、さらに汚染土壌地盤が保有している水分を勘案して水系溶媒を少なくとも20質量部以上になる量で混和して活性化混和物を原位置で調整され、  According to the present invention, the shape-processed molded product is brought into the original position by the processing equipment installed at the original position, and contaminated soil ground, contaminated soft ground, contaminated road / bank or 5 to 30 parts by mass of a modifying agent and, if necessary, 400 parts by mass or less of a function-imparting agent are added to 100 parts by mass on the basis of dry matter of contaminated agricultural land, residential land, or public land. Taking into account the water held by the ground, the activated solvent is adjusted in situ by mixing the aqueous solvent in an amount of at least 20 parts by mass,

次いで原位置で調製された活性化混和物を塊状物、杭状物、農地畦、側溝、道路、堤ないしは構造物からなる形状化処理物に加工し、次いで原位置で混和・加工された形状化処理物を原位置における環境下の常温雰囲気中に少なくとも24時間曝露養生することにより塊状体、杭状体、農地畦、側溝、道路、堤ないし構造体に無害化処理および形状化処理が施されている結着形状体である改質処理方法が提供される。  Next, the activated admixture prepared in-situ is processed into a shaped treated product consisting of a lump, pile, agricultural landfill, gutter, road, levee or structure, and then mixed and processed in-situ. The agglomerates, piles, farmland ridges, gutters, roads, levees or structures are detoxified and shaped by exposing and curing the treated material in an ambient temperature atmosphere at the original position for at least 24 hours. There is provided a modification treatment method which is a bound shaped body.

本発明によれば、前記の耐水性粉粒体品ないしは形状加工成型品が、持込位置に存在して有害物質を共存する熱履歴シリケートを乾燥物基準で100質量部に対して、改質処理剤を5ないし30質量部、必要に応じて機能付与剤を400質量部以下の量で加え、さらに熱履歴シリケートおよび改質処理剤が保有している水分を勘案して水系溶媒を少なくとも20質量部以上になる量で混和して活性化混和物を持込位置で調整され、  According to the present invention, the water-resistant granular product or the shape-processed molded product is modified with respect to 100 parts by mass on a dry matter basis of a heat history silicate that is present at the carry-in position and coexists with harmful substances. 5 to 30 parts by mass of the treatment agent, and if necessary, a function-imparting agent is added in an amount of 400 parts by mass or less, and the water-based solvent is at least 20 in consideration of the water held by the thermal history silicate and the modification treatment agent. Mix in an amount of more than part by mass and adjust the activated admixture at the carry-in position,

次いで持込位置で調製された活性化混和物を粉粒物、砂粒物、顆粒物、造粒物、硬化・固化物、構造物、管状物、線状物、多孔質体ないしは形状化物からなる耐水性粉粒体物ないしは形状加工成型物である形状化処理物に加工し、次いで持込位置で混和・加工された形状化処理物を持込位置における環境下の常温雰囲気中に少なくとも24時間曝露養生することにより粉粒体、砂粒体、顆粒体、造粒体、硬化・固化体、構造体、柱状体、管状体、線状体、板状体、膜状体、多孔質体ないしは形状化体に無害化処理および形状化処理が施されている結着形状体である改質処理方法が提供される。  Next, the activated admixture prepared at the carry-in position is water-resistant consisting of powder, sand, granules, granulated, hardened / solidified, structure, tubular, linear, porous or shaped material. Processed into a shaped processed product that is a powdered granular material or shaped processed molded product, and then exposed to the ambient temperature atmosphere in the environment at the carry-in position for at least 24 hours. Granules, sand granules, granules, granulated bodies, hardened / solidified bodies, structures, columnar bodies, tubular bodies, linear bodies, plate-like bodies, film-like bodies, porous bodies or shapes by curing There is provided a modification treatment method which is a binding shape body in which a body is subjected to a detoxification treatment and a shaping treatment.

本発明によれば、前記の改質処理剤を活用する前記の改質処理方法における混和工程で調製される流動性活性化混和物を予め用意された応用対象基材に付着せしめる加工工程により付着化処理物として調製し、次いで該付着化処理物を所定雰囲気中に開放せしめて応用対象基材と一体化された結着形状体とする養生工程で構成される一連の作業工程からなる改質処理方法において;  According to the present invention, the fluidity activated admixture prepared in the mixing step in the above-described modification processing method utilizing the above-described modification processing agent is adhered by a processing step for adhering to a prepared application target substrate. A modification comprising a series of work steps prepared by a curing process, which is prepared as a chemical treatment product, and then the adhesion treatment product is opened in a predetermined atmosphere to form a binding shape integrated with a base material to be applied. In the processing method;

上記の流動性活性化混和物が、原位置または持込位置に存在する熱履歴シリケートを乾燥物基準で100質量部に対して、改質処理剤を乾燥物基準で2ないし20質量部未満を加え、必要に応じて機能付与剤を400質量部以下の量で付加して混和して活性化混和物とし、該活性化混和物中の含有水分の含水率が35ないし70質量%範囲に確保される状態になるように水系溶媒を加えて量割合を調整して混和し、該活性化混和物が常温にて混和・放置される3時間の間のpH値が12を超える状態が確保されて可塑状、マヨネーズ状、糊状ないしはスラリー状に調製されている混和物であり;  The fluidity activated admixture is 100 parts by mass of the heat history silicate present in the original position or the carry-in position on the basis of dry matter, and 2 to less than 20 parts by mass of the modification treatment agent on the basis of dry matter. In addition, if necessary, a function-imparting agent is added in an amount of 400 parts by mass or less and mixed to make an activated admixture, and the moisture content of the water content in the activated admixture is ensured in the range of 35 to 70% by mass. As a result, an aqueous solvent is added to adjust the volume ratio so as to be in a mixed state, and the activated mixture is mixed and allowed to stand at room temperature. An admixture prepared in the form of a plastic, mayonnaise, paste or slurry;

上記の応用対象基材が、無機質材質、岩石・粘土材質、水和鉱物材質、セラミックス・窯業材質、金属材質、木材質、繊維材質、有機質材質ないしはこれら材質の複合材質からなる粉粒体、吸着性粉粒体、砂粒体、顆粒体、造粒体、硬化・固化体、構造体、床体、柱状体、管状体、線状体、板状体、膜状体、ガラクタ体ないしは形状化体であり;  The above-mentioned application target base material is an inorganic material, rock / clay material, hydrated mineral material, ceramics / ceramic material, metal material, wood material, fiber material, organic material or a composite material of these materials, adsorption Powder, sand, granule, granulated, hardened / solidified, structure, floor, columnar, tubular, linear, plate, film, galactor or shaped Is;

上記の加工工程が、上記の流動性活性化混和物を応用対象基材の表面に所定量の割合で展延、固結、結着、付着、被覆、積層、集合または注入からなる加工手段により目的・用途に応じた応用対象基材と一体化された基材付着型の活性粉体結着物、基材積層複合物、顆粒群体集合物ないしは注充填一体化物からなる付着化処理物とする工程であり;  The above processing step is performed by processing means comprising spreading, solidifying, binding, adhering, coating, laminating, assembling, or pouring the above fluid activated admixture on the surface of the substrate to be applied at a predetermined rate. A process for forming an adherent treated product comprising a base-attached active powder binder integrated with a base material to be applied according to the purpose and use, a base laminate composite, an aggregate of granules, or an injection-filled integrated body Is;

上記の養生工程が、該応用対象基材と一体化された付着化処理物を常温から100℃範囲にある常圧、加圧、減圧条件下における気中、水中、海中、土中、溶液中、蒸気中、非酸素ガス中の雰囲気の群より選ばれる単独雰囲気中ないし2種以上の組み合わせの多段雰囲気中に少なくとも15分間解放して反応・養生が進行して結着硬化の完了している基材付着型の活性粉体結着品、基材積層複合品、顆粒群体集合品ないしは注充填一体化品からなる応用対象基材と一体化された結着形状体とする工程であり;  The above curing process is performed in the atmosphere, water, sea, soil, and solution under normal pressure, pressure, and reduced pressure conditions in the range from room temperature to 100 ° C. In a single atmosphere selected from the group of atmospheres in steam and non-oxygen gas or in a multistage atmosphere of a combination of two or more, the reaction / curing progresses for at least 15 minutes to complete the binding and curing. A process for forming a binder-shaped body integrated with a base material to be applied consisting of a base-attached active powder binder, a base-layer composite, a granule aggregate assembly or an injection-filled integrated product;

上記の改質処理方法が、熱履歴シリケートを改質対象素材として、上記の一連の作業工程に付して調製される流動性活性化混和物のアルカリ性成分を固定化してpH10未満が確保され、該改質対象素材に有害物質が共存するときは該有害物質を固定・不溶化する無害化処理を施し、同時に粉粒体の熱履歴シリケートを耐水性で水中再泥化しない形状化処理を施して応用対象基材と一体化された基材付着型の結着形状体に改質処理する改質処理方法が提供される。  The above reforming treatment method uses a heat history silicate as a material to be reformed, immobilizes the alkaline component of the fluidity activated admixture prepared by the above-described series of work steps, and ensures a pH of less than 10. When harmful substances coexist in the material to be modified, a detoxification treatment is performed to fix and insolubilize the harmful substances, and at the same time, a heat history silicate of the granular material is water-resistant and shaped to prevent re-mudging in water. There is provided a modification method for modifying a substrate-attached binding shape integrated with an application target substrate.

本発明によれば、前記の活性粉体結着品が、予め混和工程で調製された可塑状、マヨネーズ状、糊状ないしはスラリー状の流動性活性化混和物を粉粒体状の応用対象基材表面に所定量の割合で付着・被覆・結着して付着化処理物とする加工工程において、該応用対象基材が比表面積100m/g以上を有する吸着性粉粒体である炭類、非晶質シリカ、活性ケイ酸、活性ケイ酸塩、珪藻土、活性アルミナ、活性アルミノケイ酸塩化合物、含炭素乾留品、吸着性焼却灰ないしはゼオライトの群より選ばれる単独ないし2種以上の組み合わせ吸着性粉粒体基材であり、According to the present invention, the active powder binder is obtained by applying a fluid, activated, admixture in the form of a powder, a plastic, mayonnaise, paste or slurry prepared in the mixing step in advance. Charcoal that is an adsorbent granular material having a specific surface area of 100 m 2 / g or more in a processing step in which the surface of the material is attached, coated, or bonded at a predetermined ratio to obtain an adhesion-treated product , Amorphous silica, activated silicic acid, activated silicate, diatomaceous earth, activated alumina, activated aluminosilicate compound, carbon-containing carbonized product, adsorptive incineration ash, or a combination of two or more selected from zeolite A powdery granular base material,

該吸着性粉粒体100質量部に対して、流動性活性化混和物の100ないしは400質量部を加えて混和しながら吸着性粉粒体基材の表面を濡らしつつ粉粒物、顆粒物ないしは形状化物である活性粉体結着物からなる付着化処理物に加工付着、被覆、結着せしめ、次いで該付着化処理物を養生工程に付する一連の作業工程により、有害化学物質を共存して粉粒体の該熱履歴シリケートが、吸着性が確保された不特定形状の粉粒体、顆粒体ないし形状化体からなる応用対象基材と固結一体化されている付着型の結着形状体である改質処理方法が提供される。  With respect to 100 parts by mass of the adsorbent granular material, 100 to 400 parts by mass of the fluidized activated admixture is added and mixed while wetting the surface of the adsorbent granular base material, and the granular material, granule or shape. In a series of work steps, the adhering treatment product consisting of the active powder binder, which is a chemical, is processed, adhered, coated, and bound, and then the adhering treatment product is subjected to a curing process. Adhesive-type bonded shaped body in which the heat history silicate of a granular body is solidified and integrated with an application target base material consisting of an unspecified powder granular body, granulated body or shaped body with ensured adsorptivity A reforming method is provided.

本発明によれば、前記の基材積層複合品が、加工工程において、混和工程で調製された可塑状、マヨネーズ状、糊状ないしはスラリー状の流動性活性化混和物を予め用意された応用対象基材の表面上に所定量の割合で応用対象基材と一体化された付着化処理物とする工程において、該応用対象基材が、無機質材質、岩石・粘土材質、水和鉱物材質、セラミックス・窯業材質、金属材質、木材質、繊維材質、有機質材質ないしはこれら材質の複合材質からなる顆粒体、造粒体、硬化・固化体、構造体、床対、柱状体、管状体、線状体、板状体、膜状体、ガラクタ体ないしは形状化体からなる形状の確保された基材であり、  According to the present invention, the base laminate composite product is an application object in which a plastic, mayonnaise, paste, or slurry fluid activated admixture prepared in the blending step is prepared in advance in the processing step. In the process of forming an adhesion-treated product integrated with the base material to be applied at a predetermined ratio on the surface of the base material, the base material to be applied is an inorganic material, rock / clay material, hydrated mineral material, ceramics・ Ceramic materials, metal materials, wood materials, fiber materials, organic materials, or granules composed of these materials, granulated bodies, hardened / solidified bodies, structures, floor pairs, columnar bodies, tubular bodies, linear bodies , A substrate having a shape made of a plate-like body, a film-like body, a rugged body or a shaped body,

該基材の表面に該流動性活性化混和物が展延、結着、付着、被覆または積層からなる加工手段により目的・用途に応じた応用対象基材と一体化された基材積層複合物らなる付着化処理物とし、次いで該付着化処理物を養生工程に付する一連の作業工程により、有害化学物質を共存して粉粒体の該熱履歴シリケートが、不特定形状の粉粒体、顆粒体ないし形状化体からなる応用対象基材と積層一体化されている付着型の結着形状体である改質処理方法が提供される。  A substrate laminate composite in which the fluidity-activated admixture is integrated with the substrate to be applied according to the purpose and application by processing means comprising spreading, binding, adhesion, coating or lamination on the surface of the substrate. Then, the heat history silicate of the granular material coexisting with harmful chemical substances is formed into an unspecified shaped granular material by a series of work steps in which the adhered processed material is subjected to a curing process. Further, there is provided a modification treatment method which is an adhesion-type binder-shaped body laminated and integrated with a base material to be applied composed of granules or shaped bodies.

本発明によれば、前記の顆粒群体集合品が、加工工程において、混和工程で調製された可塑状、マヨネーズ状、糊状ないしはスラリー状の流動性活性化混和物を予め用意された応用対象基材の表面上に所定量の割合で応用対象基材と一体化された付着化処理物とする工程において、該応用対象基材が、無機質材質、岩石・粘土材質、水和鉱物材質、セラミックス・窯業材質、金属材質、木材質、繊維材質、有機質材質ないしはこれら材質の複合材質からなる顆粒体、造粒体、ガラクタ体ないしは形状化体からなる形状の確保された顆粒状基材であり、  According to the present invention, the above-mentioned granular mass aggregate is applied to a plastic, mayonnaise, pasty or slurry fluid activated admixture prepared in the blending step in the processing step. In the process of forming an adhesion treatment product integrated with the base material to be applied at a predetermined ratio on the surface of the material, the base material to be applied is an inorganic material, a rock / clay material, a hydrated mineral material, a ceramic material, It is a granulated base material having a shape made of ceramic material, metal material, wood material, fiber material, organic material or a composite material of these materials, a granulated material, a crushed material or a shaped material,

該基材の表面に該流動性活性化混和物が混和、結着、付着、被覆または積層からなる加工手段により目的・用途に応じた顆粒状の応用対象基材と一体化された顆粒群体集合物からなる付着化処理物とし、次いで該付着化処理物を養生工程に付する一連の作業工程により、有害化学物質を共存して粉粒体の該熱履歴シリケートが、不特定形状の粉粒体、顆粒体ないし形状化体からなる応用対象基材と一体化されている付着型の結着形状体である改質処理方法が提供される。  Granule mass assembly in which the fluidized activated admixture is integrated with a granular application target substrate according to the purpose and application by processing means comprising mixing, binding, adhesion, coating or lamination on the surface of the substrate The heat history silicate of the granular material coexisting with harmful chemical substances is formed into a non-specifically shaped powder particle by a series of work steps in which the adhered processed material is subjected to a curing process. There is provided a modification treatment method which is an adhesion-type binder-shaped body integrated with a base material to be applied comprising a body, a granule or a shaped body.

本発明によれば、前記の注充填一体化品が、有害物質類もしくは低レベルの放射性物質を共存している顆粒状またはガラクタ状類の塊状物からなる顆粒群集合体、また既存の無機質である顆粒状ないしガラクタ状の塊状物からなる小塊群集合体を容器に収納した容器収納ガラクタ集合群体からなる応用対象基材と一体化された付着化処理物とする工程において、  According to the present invention, the injection-filled integrated product is a granular group aggregate composed of granular or galactic aggregates coexisting harmful substances or low-level radioactive substances, or an existing inorganic substance. In the step of making the adhesion treatment product integrated with the application target base material composed of the container-containing galactor aggregate group in which the small aggregate group aggregate composed of granular or garlic aggregates is stored in the container,

該容器収納ガラクタ集合群体の収めてある容器中に流動性活性化混和物を容器中全体に注入充填してガラクタ集合群体からなる応用対象基材と一体化された注充填一体化物からなる付着化処理物とし、次いで該付着化処理物を養生工程に付する一連の作業工程により、有害化学物質を共存して粉粒体の該熱履歴シリケートが、不特定形状の粉粒体、顆粒体ないし形状化体からなる応用対象基材と一体化されている付着型の結着形状体である改質処理方法が提供される。  The fluidized activated admixture is injected and filled into the container in which the container-accommodating lumpy aggregates are contained, and the adhesive is formed by an injection-filled integrated product integrated with the base material to be applied consisting of the galactic aggregates. The heat history silicate of the granular material coexisting with harmful chemical substances is formed into a processed product and then subjected to the curing process, and then the adhering processed material is formed into an unspecified shaped granular material, granular material or A modification treatment method is provided which is an adhesion-type binding shape body integrated with a base material to be applied composed of a shaped body.

本発明によれば、前記の改質処理剤を活用して、休眠成分からなる熱履歴シリケートを改質対象素材とし、少なくとも常温における前記の改質処理方法に付して、pH12が確保されている活性化混和物を調製し、さらに必要に応じて形状化処理物ないしは付着化処理物を調製し、  According to the present invention, by utilizing the above-described modification treatment agent, a heat history silicate composed of a dormant component is used as a material to be modified, and at least the above-described modification treatment method at room temperature is used to ensure a pH of 12. An activated admixture, and, if necessary, a shaped or adhering treatment,

次いで活性化混和物、ないしは形状化処理物または付着化処理物におけるアルカリ性成分を固定化してpH10未満が確保され、該改質対象素材に有害物質が共存するときは該有害物質を中性域ならびに酸性域における溶出試験で環境基準値以下の範囲に固定・不溶化する無害化処理が施され、同時に粉粒体の熱履歴シリケートを耐水性で水中再泥化しない形状化処理が施されている自己完結型の原位置非成型品、耐水性粉粒体品、形状加工成型品、さらに基材付着型の活性粉体結着品、基材積層複合品、顆粒群体集合品または注充填一体化品である結着形状体が提供される。  Next, when the alkaline component in the activated admixture, or the shaped treatment product or the adhesion treatment product is immobilized and pH of less than 10 is secured, and the harmful substance coexists in the material to be modified, the harmful substance is neutralized as well as Self-detoxification treatment that fixes and insolubilizes within the environmental standard value or less in the elution test in the acidic range, and at the same time, the heat history silicate of the granular material is water-resistant and shaped to prevent re-mudging in water Completed in-situ non-molded product, water-resistant granular product, shape-processed molded product, base material-attached active powder binder product, base material laminated composite product, granule group assembly product or injection-filled integrated product A binding shape is provided.

本発明によれば、前記の原位置非成型品が、原位置に存在して有害元素群ないしダイオキシン類を環境基準値以上の量で共存して汚染している土壌地盤、軟弱地盤、道路・堤・法面ないしは農地・宅地・工業用地・公共用地を改質対象素材とし、少なくとも常温において改質処理剤を活用する一連の作業工程からなる改質処理方法に付して、有害元素群ないしダイオキシン類を共存して粉粒体の該熱履歴シリケートが、外圧に変動性を示す状態に結着・硬化して水中再泥化しない耐水性の有用土壌地盤、軟弱地盤、道路・堤・法面ないしは農地・宅地・公共用地に無害化処理ならびに形状化処理が施されている結着形状体が提供される。  According to the present invention, the in-situ non-molded product is in situ, contaminated with soil elements, soft grounds, roads and soils that coexist and contaminate harmful elements or dioxins in an amount greater than the environmental standard value. A dam, slope, or farmland / residential land / industrial land / public land is used as a material to be reformed. Water-resistant useful soil ground, soft ground, road, levee, and method where the heat history silicate of the granular material coexisting with dioxins is bound and hardened in a state of variability in external pressure and does not re-mudder in water Provided is a binding shape body that is subjected to detoxification treatment and shaping treatment on a surface, farmland, residential land, or public land.

本発明によれば、前記の形状加工成型品が、原位置に存在して有害元素群ないしダイオキシン類を環境基準値以上の量で共存して汚染されている土質土壌、建築・土木関連廃土、窯業関連廃物、ケイ酸塩系投棄廃棄物類、汚泥・底質・脱水ケーキ類、焼却灰類を改質対象素材とし、原位置で少なくとも常温において改質処理剤を活用する一連の作業工程からなる改質処理方法に付して、有害元素群ないしはダイオキシン類を共存して粉粒体の該熱履歴シリケートが、一軸圧縮強度で500KN/m以上の強度が確保される状態に結着・硬化して水中再泥化しない耐水性の塊状体、杭状体、農地畦、側溝、道路、堤ないし構造体に無害化処理ならびに形状化処理が施されている結着形状体が提供される。According to the present invention, the shape-processed molded product is soil soil, building / civil engineering-related waste soil that is present in situ and contaminated with harmful elements or dioxins coexisting in an amount exceeding the environmental standard value. A series of work processes that utilize reforming treatment agents at least at normal temperature at the normal temperature, using ceramic-related waste, silicate dumping waste, sludge / sediment / dehydrated cakes, and incinerated ash The thermal history silicate of the granular material is bound in a state in which a uniaxial compressive strength of 500 KN / m 2 or more is ensured in the presence of a harmful element group or dioxins.・ Binder-shaped bodies that have been detoxified and shaped to water-resistant masses, piles, farm ridges, gutters, gutters, roads, dikes, or structures that are hardened and not re-mudged in water are provided. The

本発明によれば、前記の形状加工成型品が、原位置または持込位置に存在して有害化学物質を共存する熱履歴シリケートを改質対象素材とし、少なくとも常温で改質処理剤を活用する一連の作業工程からなる改質処理方法に付して、有害化学物質を共存して粉粒体の該熱履歴シリケートが、一軸圧縮強度で500KN/m以上の強度が確保される状態に結着・硬化して水中再泥化しない耐水性の粉粒体、砂粒体、顆粒体、造粒体、硬化・固化体、構造体、柱状体、管状体、線状体、板状体、膜状体、多孔質体ないしは形状化体に無害化処理ならびに形状化処理が施されている結着形状体が提供される。According to the present invention, the shape-processed molded product uses a heat treatment silicate that exists in an original position or a bring-in position and coexists with a harmful chemical substance as a material to be modified, and uses a modifying treatment agent at least at room temperature. It is subjected to a reforming method consisting of a series of work steps, and the thermal history silicate of the granular material coexisting with harmful chemical substances is connected to a state in which a uniaxial compressive strength of 500 KN / m 2 or more is secured. Water-resistant granules, sand granules, granules, granules, cured / solidified bodies, structures, columns, tubular bodies, linear bodies, plates, membranes Provided is a bound-shaped body, a porous body, or a shaped body that has been subjected to detoxification treatment and shaping treatment.

本発明によれば、前記の耐水性粉粒体品が、原位置または持込位置に存在して有害化学物質を共存する熱履歴シリケートを改質対象素材とし、少なくとも常温で改質処理剤を活用する一連の作業工程からなる改質処理方法に付して、有害化学物質を共存して粉粒体の該熱履歴シリケートが、砂粒状ないし顆粒状の再生砂、再生土、再生骨材、流動化処理材、覆砂材、中込材、造成材、盛土材、築堤材、土壌改良材、客土材の群からなる土木用資材、また植栽用土、造園用資材、緑化基盤材、目土の群からなる植物育成資材からなる無害化処理ならびに形状化処理が施されている結着形状体が提供される。  According to the present invention, the water-resistant granular product is a material to be reformed, which is a heat history silicate that is present in the original position or in the carry-in position and coexists with harmful chemical substances, and at least at room temperature, It is subjected to a reforming treatment method consisting of a series of work steps to be utilized, and the thermal history silicate in the form of granular materials coexisting with harmful chemical substances is regenerated sand, regenerated soil, regenerated aggregate, Fluidization treatment materials, sand-capping materials, medium-filled materials, construction materials, embankment materials, embankment materials, soil improvement materials, materials for civil engineering consisting of groups of guest soil materials, planting soil, landscaping materials, greening base materials, eyes Provided is a binding shape body that has been subjected to a detoxification treatment and a shaping treatment made of a plant-growing material made of a group of soil.

本発明によれば、前記の形状加工成型品が、持込位置に存在する熱履歴シリケート、ないしは有害物質を共存する熱履歴シリケートを改質対象素材とし、予め混和工程において糊状ないし可塑状に調製されている流動性活性化混和物を調製し、該流動性混和物をプラスチック製の基材・型類表面に1ないしは20mm厚の膜状、板状、塗膜状もしくはフィルム状の膜状物とし、養生工程において養生条件下で養生した後、基材・型類より脱着せしめる一連の作業工程からなる改質処理方法に付することにより、有害化学物質を共存して粉粒体の該熱履歴シリケートが、不定形ないし定形の膜状、板状、フイルム状の膜状資材からなる無害化処理ならびに形状化処理が施されている結着形状体が提供される。  According to the present invention, the shape-processed molded product is a heat history silicate present in the carry-in position or a heat history silicate coexisting with a harmful substance as a material to be modified, and is previously paste-like or plasticized in the mixing step. The prepared fluidity-activated admixture is prepared, and the fluidity admixture is formed on the surface of a plastic substrate or mold, in the form of a film, plate, film, or film having a thickness of 1 to 20 mm. After being cured under curing conditions in the curing process, it is subjected to a reforming process consisting of a series of work processes that are desorbed from the substrate and molds, so that harmful chemical substances can coexist and the powder is Provided is a binding shape body in which the heat history silicate is subjected to a detoxification treatment and a shaping treatment, which are made of a film-like material having an amorphous shape or a fixed shape, a plate shape, or a film shape.

本発明によれば、前記の形状加工成型品が、持込位置に存在して有害物質を共存して、含水比が150より大きい含水ヘドロ・底質類または農業集落排水・上水・下水の汚泥類であるときは予め含水比150未満に脱水処理もしくは既に含水比150未満である含水汚泥類を改質対象素材とし、少なくとも常温において改質処理剤を活用する一連の作業工程からなる改質処理方法に付することにより、有害化学物質を共存して粉粒体の該熱履歴シリケートが、一軸圧縮強度で500KN/m以上の強度が確保される状態に結着・硬化して水中再泥化しない耐水性の粉粒体、砂粒体、顆粒体、硬化体、構造体、固化体、成型体、膜状体、形状体、フイルム・膜状体、機能性保有被覆体、積層・塗布体、顆粒群集合体ないしは注充填一体化体に無害化処理ならびに形状化処理が施されている結着形状体が提供される。According to the present invention, the shape-processed molded product is present in the carry-in position, coexists with harmful substances, and contains water-containing sludge / sediments or agricultural settlement wastewater / wastewater / sewage with a water content ratio greater than 150. When it is sludge, it is dehydrated to a water content ratio of less than 150 in advance, or water sludge that already has a water content ratio of less than 150 is used as a material to be reformed, and reforming consists of a series of work steps that utilize a reforming treatment agent at least at room temperature. By applying the treatment method, the thermal history silicate of the granular material coexisting with harmful chemical substances is bound and cured to a state where a uniaxial compressive strength of 500 KN / m 2 or more is ensured, and the Water-resistant powder, sand granule, granule, hardened body, structure, solidified body, molded body, film-like body, shaped body, film / film-like body, functional holding coating, lamination / coating Body, granule group aggregate, or cast filling integrated body A binding shape body that has been subjected to detoxification treatment and shaping treatment is provided.

本発明によれば、前記の含水の底質もしくは農業集落排水・上水・下水の汚泥が、水に分散している含水土質・汚泥・アオコ・藻類群からなる浮遊物に対して、ファンクショメントである沈降凝集組成物を水中に撒布して加え撹拌して、水分散性の浮遊物を水中で予め凝集沈降せしめ、水中底部底質として回収される含水泥土類からなる改質対象素材とし、少なくとも常温において改質処理剤を活用する一連の作業工程からなる改質処理方法に付に付して、該熱履歴シリケートに無害化処理ならびに形状化処理が施されている形状加工成型品である結着形状体が提供される。  According to the present invention, the above-mentioned bottom sediment of water or sludge of agricultural settlement drainage, clean water, and sewage is subjected to a function against suspended matter composed of hydrous soil, sludge, blue sea, algae group dispersed in water. Disperse the sedimentation and agglomeration composition, which is a mentament, in water and stir to pre-aggregate and disperse the water-dispersible suspended matter in water in advance. A shape processing molded product in which the heat history silicate is subjected to a detoxification process and a shaping process at the same time as a modification processing method comprising a series of work steps utilizing a modifying treatment agent at least at room temperature. A binding shape is provided.

含リン焼却灰
本発明によれば、前記の耐水性粉粒体品ないしは形状加工成型品が、持込位置に存在して有害元素群を環境基準値以上の量で共存して汚染されており、リン成分を含有する下水や農業集落排水の含水汚泥の焼却灰を水分調整剤として下水や農業集落の含水汚泥に加えて混合され、さらに必要に応じてファンクショメントの機能付与組成物である消臭剤類を加えて調整混合されている下水・農業集落排水の焼却灰が複合している熱履歴シリケートであり、該有害物質共存の改質対象素材に改質処理剤を活用する一連の作業工程からなる改質処理方法に付することにより、有害化学物質を共存して粉粒体の該熱履歴シリケートが、植物育成材、緑化基盤材、目土材、客土材、埋戻材、土質作業性改良材ないしは土壌改良材に無害化処理および形状化処理が施されている結着形状体が提供される。
Phosphorus-containing incinerated ash According to the present invention, the above-mentioned water-resistant granular product or shape-processed molded product is present in the carry-in position and contaminated with a harmful element group in an amount exceeding the environmental standard value. In addition, incinerated ash of water-containing sludge from sewage and agricultural settlement drainage containing phosphorus components is added to the water-containing sludge from sewage and agricultural villages as a moisture control agent, and further, if necessary, a function-imparting composition This is a heat history silicate compounded with incineration ash from sewage and agricultural village effluent that has been adjusted and mixed by adding deodorants. By applying to the reforming treatment method consisting of the work process, the thermal history silicate of the granular material coexisting with the harmful chemical substance, plant growth material, greening base material, joint material, customer soil material, backfill material , Detoxification treatment for soil workability improver or soil improver A binding shape body that has been treated and shaped is provided.

機能付与剤が活性化成分に補足されている処理材
本発明によれば、前記の形状加工成型品が、持込位置に存在して有害物質を共存する熱履歴シリケートを改質対象素材とし、改質処理剤100質量部に対して、機能付与剤であるファンクションメントである耐熱火組成物ないし断熱・保温組成物を100質量部以上の量で付加補足されている機能付加成分を活用する一連の作業工程からなる改質処理方法に付することにより、有害化学物質を共存して粉粒体の該熱履歴シリケートが、不焼成または焼成された特定または不特定の耐熱・保温築炉材、セラミックス品、レンガ・耐火材・断熱材ないしは保温・断熱材とする無害化処理および形状化処理が施されている結着形状体が提供される。
According to the present invention, the shape-processed molded product is a heat history silicate that is present at the carry-in position and coexists with harmful substances, and is a material to be modified. A series of utilizing a function-added component supplemented with an amount of 100 parts by mass or more of a heat-resistant fire composition or a heat-insulating / heat-retaining composition as a function-imparting function with respect to 100 parts by mass of the modification treatment agent. The heat history silicate of the granular material coexisting with toxic chemical substances is subjected to a reforming treatment method comprising the above-described work process, and the specific or unspecified heat-resistant and heat-retaining furnace material that has not been fired or fired, There is provided a bonded shape body that has been subjected to a detoxification process and a shaping process as a ceramic product, a brick, a refractory material, a heat insulating material, or a heat insulating and heat insulating material.

本発明によれば、前記の形状加工成型品が、持込位置に存在して有害物質を共存する熱履歴シリケートを改質対象素材とし、改質処理剤100質量部に対して、機能付与剤であるファンクションメントの断熱・保温組成物、または10m/g以上の比表面積を有し0.05ないし1.2g/ccの範囲にあるかさ密度を有し、耐熱性の繊維状ないし粉粒体状のシリケートまたはケイ酸塩組成物からなるケイ酸カルシウム系化合物ないし保温・断熱材の廃材を100質量部以上の量で添加補足の改質処理剤を活用する一連の作業工程からなる改質処理方法に付することにより、有害化学物質を共存して粉粒体の熱履歴シリケートが、不焼成または焼成された特定または不特定の保温・断熱材、セラミックス品、レンガ・耐火材・断熱材とする無害化処理および形状化処理が施されている結着形状体が提供される。According to the present invention, the shape-processed molded product is a heat history silicate that is present at the carry-in position and coexists with harmful substances, and the function-imparting agent is used with respect to 100 parts by mass of the modification treatment agent. A heat insulation fiber or powder having a specific surface area of 10 m 2 / g or more and having a bulk density in the range of 0.05 to 1.2 g / cc Reformation consisting of a series of work steps utilizing a supplementary modification treatment agent added with a calcium silicate-based compound consisting of a body-like silicate or silicate composition or waste material of heat insulation / insulation material in an amount of 100 parts by mass or more By applying to the treatment method, specific or unspecified heat-retaining / insulating materials, ceramic products, bricks, refractory materials, and heat insulating materials, in which the thermal history silicate of the granular material coexists with harmful chemical substances, is not fired or fired Toss Binder shape body detoxification and shaping treatment is applied is provided.

活性粉体結着品
本発明によれば、前記の活性粉体結着品が、予め調製された可塑状、マヨネーズ状、糊状ないしスラリー状の流動性活性化混和物を粉粒体応用対象基材表面上に所定量の割合で応用対象基材と固結一体化された付着化処理物とする加工工程において、該応用対象基材が比表面積100m/g以上を有する吸着性粉粒体である炭類、非晶質シリカ、活性ケイ酸、活性ケイ酸塩、珪藻土、活性アルミナ、アルミノケイ酸塩化合物、含炭素乾留品、吸着性焼却灰ないしはゼオライトの群より選ばれる単独ないし2種以上の組み合わせ吸着性粉粒体基材に対して、
Active powder binder product According to the present invention, the above-mentioned active powder binder product is prepared by applying a pre-prepared plastic, mayonnaise, paste or slurry fluidized activated admixture. An adsorbent powder having a specific surface area of 100 m 2 / g or more in a processing step for forming an adhesion-treated product consolidated and integrated with a base material to be applied at a predetermined ratio on the surface of the base material. Carbon or amorphous silica, activated silica, activated silicate, diatomaceous earth, activated alumina, aluminosilicate compound, carbon-containing carbonized product, adsorptive incineration ash or zeolite, or one or two kinds For the above combined adsorptive powder base material,

該流動性活性化混和物を加えて混和して粉粒体応用対象基材表面を濡らしつつ粉粒物、顆粒物ないし形状化物である付着化処理物を経て付着、被覆、結着せしめる一連の作業工程により、粉粒体応用対象基材の吸着性が確保されて固結一体化された不特定形状の粉粒体、顆粒体ないし形状化体からなる結着形状体が提供される。  A series of operations in which the fluidized activated admixture is added and mixed to wet the surface of the base material subject to application of the granular material, and then adhere, coat, and bind through the adhering treatment product that is a granular material, granule, or shaped product. By the process, an adhering shaped body composed of an unspecified powder, granule, or shaped body, which is secured and integrated with the adsorbability of the powder application target base material, is provided.

基材積層複合品
本発明によれば、前記の基材積層複合品が、持込位置に存在する熱履歴シリケート、ないしは有害物質を共存する熱履歴シリケートを改質対象素材とし、予め前記混和工程において糊状ないしは可塑状に調製されている流動性活性化混和物からなる糊状結着剤を調製し、該流動性混和物を予め用意された無機質資材、岩石・粘土類、窯業資材、木、繊維質、有機質、金属ないしは素材の複合素材により形成されている成型体、造成体ないしは型類体からなる基材類表面に塗装、接着、結着、被覆、多層塗り、どぶ浸け、まぶし、貼り付け、塗りつけ、吹き付け、流し込み、注入手段により塗布・被覆・結着せしめて積層加工層を形成複合せしめ、
According to the present invention, the above-mentioned base laminate composite product is a heat history silicate that exists at the carry-in position or a heat history silicate that coexists with harmful substances as a material to be modified, and the mixing step is performed in advance. Prepared a paste-like binder composed of a fluid activated admixture prepared in paste or plastic form, and prepared the inorganic material, rocks / clays, ceramics material, wood, etc. , Coating, bonding, binding, coating, multilayer coating, soaking, dusting, etc. on the surface of the base material made of composite material of fiber, organic material, metal or material Pasting, painting, spraying, pouring, applying, coating and binding by injection means to form a composite layer,

塗布物、被覆物、付着物、結着物、床状物または積層物からなる基材積層複合物とする一連の作業工程からなる改質方法に付することにより、有害化学物質を共存して粉粒体の該熱履歴シリケートが、剪断破壊付着力において200KN/m以上の付着力で確保された塗布体、被覆体、付着体、結着体、床状態もしくは積層体とする無害化処理および形状化処理が施されている結着形状体が提供される。By subjecting it to a reforming method consisting of a series of work steps to make a substrate laminate composite consisting of a coating, covering, deposit, binder, flooring or laminate, it is possible to coexist with harmful chemical substances and powder Detoxification treatment in which the heat history silicate of the granules is secured with an adhesive strength of 200 KN / m 2 or more in terms of shear fracture adhesive strength to form an applied body, a covering body, an adhesive body, a bound body, a floor state, or a laminated body, and A bound shape body that has been shaped is provided.

本発明によれば、前記の基材積層複合品において、予め調製された前記流動性混和物からなる糊状結着剤が、水系溶媒を介して、前記組成式(1)または(2)で表されるケイ酸アルカリの粉粒体ないし水混和体である活性化成分を改質して調製して、持込位置に存在して有害物質を共存する粉状体を改質対象素材として、一連の作業工程からなる改質方法に付することにより、pH4の酸性溶液に浸漬したとき固化体強度保持率が少なくとも80%確保されている塗布体、被覆体、付着体、結着体、成型体、床状体もしく積層体とする無害化処理ならびに形状化処理が施されている耐酸性の基材積層複合品である結着形状体が提供される。  According to the present invention, in the base laminate composite product, the paste-like binder composed of the fluid admixture prepared in advance is expressed by the composition formula (1) or (2) via an aqueous solvent. Prepared by modifying the activated component, which is an alkali silicate powder or water blend, represented as a material to be modified, a powder that exists at the carry-in location and coexists with harmful substances, By applying the modification method consisting of a series of work steps, a coated body, a coated body, an adherent body, a bound body, and a molded body that have a solidified body strength retention of at least 80% when immersed in an acidic solution of pH 4 Provided is a binding shape body which is an acid-resistant base material laminated composite product which has been subjected to detoxification treatment and shaping treatment to form a body, a floor-like body or a laminate.

本発明によれば、前記顆粒群体集合品が、前記の顆粒体または骨材からなる顆粒群集合体、または既存無機質で粒径が2ないし12mmφでかさ密度が0.2ないし3.5g/ccの球状、中空状、円柱状、フレーク状、顆粒状、不特定粒状、骨材状、不特定粒状、ガラクタ状または粉粒状の集合群体を骨格素材として選び、持込位置に存在して有害物質を共存する改質対象素材を活用して予め流動性混和物を調製し、  According to the present invention, the aggregate of granule aggregates is a granule aggregate composed of the granules or aggregates, or a spherical particle having a particle size of 2 to 12 mmφ and a bulk density of 0.2 to 3.5 g / cc. , Hollow, cylindrical, flake, granular, unspecified granular, aggregated, unspecified granular, garlic or powdery aggregates are selected as skeletal materials and coexist with harmful substances Prepare the fluid admixture in advance using the material to be modified,

該骨格素材で構成される集合群体の表面全体を濡らせる量で該流動性混和物を加え、群体粒子の表面全体を結着剤で被覆・結着して集合群体を集合群体形状物とする一連の作業工程からなる改質方法に付することにより顆粒体等の集合群体が一体化した粟オコシ状集合群体形状体として無害化処理ならびに形状化処理が施されている結着形状体が提供される。  The flowable admixture is added in an amount that wets the entire surface of the aggregated body composed of the skeletal material, and the entire surface of the aggregated particles is coated and bound with a binder to make the aggregated group shaped object. By providing a reforming method consisting of a series of work steps, a binding shaped body that has been subjected to detoxification treatment and shaping treatment is provided as a cocoon-like aggregate assembly shape in which aggregate assemblies such as granules are integrated Is done.

本発明によれば、前記の顆粒体または骨材からなる顆粒群集合体、また既存の無機質である顆粒状ないしガラクタ状の有害物質類を共存する廃棄物類もしくは低レベルの放射性物質を共存している集合群体を容器に収納した容器収納ガラクタ集合群体に対して、水系溶媒による分散性混和物であり、必要に応じてインプルーブメントであるバリウム塩組成物の配合されたスラリー状混和物を注入充填による一連の作業工程からなる改質方法に付することにより、低レベルの放射性物質ないしは普通物質の集合群体が容器の中に封じ込められて一体化された状態に無害化処理ならびに形状化処理が施されている注充填一体化品である結着形状体が提供される。  According to the present invention, the aggregates of granules or aggregates composed of the above-mentioned granules or aggregates, and wastes or existing low-level radioactive substances coexisting with existing inorganic granular or trash-like harmful substances. Inject and fill a container-containing debris group that contains the aggregates in a container with a slurry-like mixture containing a barium salt composition that is a dispersible admixture with an aqueous solvent and, if necessary, an improvement. By applying the reforming method consisting of a series of work steps according to the above, detoxification processing and shaping processing are performed in a state in which a group of low-level radioactive substances or ordinary substances is contained in a container and integrated. A bonded shape body is provided which is an integrated product filled with pouring.

再資源化資材
本発明の効果は、大量に発生して今後も増量発生が予想され、処理・処分に窮している有害物質を共存する廃棄物類に対して、特定される改質処理剤を一連の作業工程で構成される改質処理方法に付することにより、廃棄物類をpH10未満で有害元素類の溶出が中性域のみならず酸性雨を想定する酸性域における溶出も抑制され、同時に所定強度が確保されて水中再泥化が阻止された結着形状体に改質処理し、環境に低負荷型で低価格にて安全に再資源化資材である趣向資材、生活資材、工業用資材、建材、土木資材、自然環境資材ないしは緑化・造園資材等として供給できることから廃棄物類の再生利用が可能となり、循環型社会の構築を可能とし、ならびに環境問題および廃棄物問題等の解消に貢献できるところにある。
Recycled material The effect of the present invention is a reforming agent that is specified for wastes that are generated in large quantities and are expected to increase in the future and coexist with hazardous substances that are in the process and disposal. Is applied to the reforming method consisting of a series of work steps, and the leaching of hazardous elements at a pH of less than 10 is suppressed not only in the neutral range but also in the acidic range assuming acid rain. At the same time, it is reformed into a binding shape that has a predetermined strength and prevents re-mudging in the water, and it is an environmentally friendly material that is a resource-recycling material that is low-load and safe at a low price. Since it can be supplied as industrial materials, building materials, civil engineering materials, natural environmental materials, or greening / landscaping materials, etc., it becomes possible to recycle wastes, to build a recycling-oriented society, as well as environmental issues and waste issues, etc. There is a place that can contribute to the resolution.

[本発明に至った経過]
本発明者等は、大量にして確実に発生して処理・処分に窮している廃棄物類から水溶出する有害元素群のホウ素ないしはフッ素、さらに同時に溶出する重金属類(カドミニウム、砒素、水銀、鉛、クロム、セレン)、また各種の廃棄物類に共存するダイオキシン類を特別な熱エネルギーや高価な特別設備をセットすることなく、少なくとも常温において環境に低負荷型で無害化処理して、有害元素群を中性域のみならず酸性域においても水不溶性に固定化し、ダイオキシン類を分解無害化して廃棄物類を再生利用可能な耐水性の結着形状体として提供できる改質技術を確立することは、環境問題における課題を解消できることから重要であると判断した。
[Proceeding to the present invention]
The inventors of the present invention have developed a harmful element group such as boron or fluorine that is eluted in water in a large amount and is treated and disposed of, and heavy metals that are eluted simultaneously (cadmium, arsenic, mercury, Lead, chromium, selenium) and dioxins coexisting in various wastes are harmless by detoxifying them at least at room temperature with no special heat energy or expensive special equipment. Establish a reforming technology that can fix the element group to be water-insoluble not only in the neutral region but also in the acidic region, detoxify the dioxins, and provide waste as a water-resistant binding shape. This is important because it can solve the problems in environmental problems.

そのため従来技術により廃棄物類から水溶出する有害な元素群を水不溶性に処理する手段の例においては、廃棄物類の処理剤であるセメント等に有害物質が共存していたり、処理剤を多量に使用せねばならず、多種類の処理対象有害物質に多種類の薬剤に採択が必要であったり、複数の作業工程が必要であったり、また処理された処理品が自然環境条件に(紫外線や酸性雨等)に不安定であったり課題を残してきた。  For this reason, in the example of means for treating a harmful element group that is eluted from wastes with water by using conventional technology, water is insoluble. Must be used for many kinds of hazardous substances to be treated, multiple kinds of drugs must be adopted, multiple work steps are required, and the treated products must be subjected to natural environmental conditions (UV Or acid rain, etc.) and have left problems.

特に、従来技術である本発明者等の先願技術(特開2002−128550)における処理方法により廃棄物類から溶出する有害元素群に対処する時は、廃棄物類を構成している休眠成分のケイ酸塩系化合物を活性化させるために、例えば処理対象の廃棄物類100質量部に対してアルカリ系硬化剤を少なくとも20質量と多量のアルカリ性成分を加えて処理しており、しかも廃棄物類に共存する有害元素群を単一性状の元素群として一括して一律に処理するために多量のアルカリ成分からなる処理剤を使用してきた。しかも、多量のアルカリには充分可溶であるであるホウ素や酸類元素であるフッ素を不溶化対象元素として、他の重金属類と同時に不溶化せしめる技術の開示はない。  In particular, when dealing with a group of harmful elements eluted from wastes by the processing method in the prior art of the present inventors (Japanese Patent Laid-Open No. 2002-128550), which is a prior art, a dormant component constituting the wastes In order to activate the silicate-based compound, for example, 100 parts by mass of the waste to be treated is treated by adding at least 20 mass of an alkaline curing agent and a large amount of an alkaline component, and waste In order to treat the harmful element group coexisting in the same group as a single element group in a lump, a treating agent composed of a large amount of alkali components has been used. In addition, there is no disclosure of technology for insolubilizing simultaneously with other heavy metals using boron, which is sufficiently soluble in a large amount of alkali, or fluorine, which is an acid element, as an element to be insolubilized.

本発明者等は、以上の従来技術等を充分に検討した結果、まず改質対象素材の休眠成分を活性化に必要にして充分な量であるpH12を超えるアルカリ性成分を加える混和工程において、休眠成分を活性化させると共に休眠成分の活性化により遊離するアルカリ成分を可能な範囲で消費せしめて系内における遊離アルカリ成分を可能な限り少量に減少せしめることにより、改質対象素材から溶出する有害元素群を溶解せしめず、有害元素群の固定・不溶化を可能とする水不溶性鉱物を有効に形成せしめ、またダイオキシン類の分解し、同時に粉粒体の改質対象素材を再資源化資材として各分野に供給可能な物性を備えた改質処理資材に改質処理するためには、改質処理剤における役割分担と量条件を明確にした一連の作業工程が必要であると判断した。  As a result of thorough examination of the above prior art and the like, the present inventors first made a dormancy in the mixing step of adding an alkaline component exceeding pH 12, which is a sufficient amount necessary for activating the dormant component of the material to be modified. Harmful elements eluted from the material to be modified by activating the components and consuming as much alkaline components as possible by activating dormant components to reduce the free alkali components in the system as little as possible. Effectively form water-insoluble minerals that enable the fixation and insolubilization of harmful element groups without dissolving the group, dioxins are decomposed, and at the same time, the material to be reformed is used as a recycling material in various fields In order to modify the modified material with the physical properties that can be supplied to it, a series of work steps that clarify the role assignment and amount conditions in the modifying agent are necessary. It was cross-sectional.

その上で本発明者等は、改質対象素材となる廃棄物類から溶出する有害な元素群を同一カテゴリーにある一括グループとして一律に処理してきた技術に課題があると判断した。したがって本発明者等は、この課題に対応するために有害元素群を性状別にグループ分類し、まず分類されたグループ別の処理対応技術を検討した。その結果、本発明者等は、まず処理対象となる有害な元素群のグループ分類として、純粋な塩基性成分として挙動する塩基性元素群であるカドミニウムならびに水銀からなるグループ、またオキソ酸を形成するオキソ酸元素群である鉛、クロム、ヒ素、セレンならびにホウ素からなるグループ、さらにハロゲン酸として活動する酸類元素であるフッ素からなる三つのグループに分類することが妥当であると判断した。  In addition, the present inventors have determined that there is a problem in the technology that has uniformly processed the harmful element groups eluted from the wastes to be reformed as a collective group in the same category. Therefore, in order to cope with this problem, the present inventors classified the harmful element groups into groups according to the properties, and first examined processing techniques for each classified group. As a result, the present inventors first form a group consisting of cadmium and mercury, which are basic element groups that behave as pure basic components, and an oxo acid as a group classification of harmful element groups to be treated. It was judged appropriate to categorize into the group consisting of lead, chromium, arsenic, selenium and boron, which are oxoacid elements, and three groups consisting of fluorine, which is an acid element that acts as a halogen acid.

本発明者等は、異なる性状を示す各グループの元素群に対して、それぞれの性状に適切に対応できる固定・不溶化機構と処理条件を求めて検討し、各グループに対応する個別の固定・不溶化処理条件を見出し、その個別の固定・不溶化条件を全て満足する改質処理剤による廃棄物類の改質条件を見出した。特に、本発明の改質効果が、自然界の酸性雨を想定した条件下でも不溶化処理が有効に発揮できる改質技術を見出した。  The inventors of the present invention have studied and studied the fixing / insolubilization mechanism and processing conditions that can appropriately correspond to each element for each group of elements having different properties, and individually fixed / insolubilized corresponding to each group. The processing conditions were found, and the reforming conditions of the wastes by the reforming agent satisfying all the individual fixing / insolubilizing conditions were found. In particular, the present inventors have found a modification technique in which the modification effect of the present invention can effectively perform the insolubilization treatment even under conditions assuming acid rain in nature.

以上の判断に基づき、廃棄物類の処理技術に関して鋭意検討・実験を重ねた。その結果、本発明者らは、塩基性成分のカドミニウムならびに水銀からなるグループは、充分なアルカリ性の許でのアルミノケイ酸塩の形成が必要であることが確認された。一方、オキソ酸を形成する鉛、クロム、ヒ素、セレン、ホウ素からなるグループは、過剰のアルカリ成分と接する時は、このグループ金属類は水溶解性を高める傾向にあり、グループ金属を固定・不溶化するには、充分ではあるが過剰でないアルカリの存在下でアルミノケイ酸塩を形成させる必要であることが確認された。さらにハロゲン酸であるフッ素からなるグループは、充分なカルシウム成分の存在下において、フッ化カルシウムやケイフッ化カルシウム等のアパタイト鉱物の形成が必要であることが確認された。  Based on the above judgment, we conducted extensive studies and experiments on waste disposal technologies. As a result, the present inventors have confirmed that the group consisting of the basic components cadmium and mercury needs to form an aluminosilicate with sufficient alkalinity. On the other hand, the group consisting of lead, chromium, arsenic, selenium, and boron that form oxo acid tends to increase water solubility when it comes into contact with an excessive alkali component. It was confirmed that it was necessary to form the aluminosilicate in the presence of sufficient but not excessive alkali. Furthermore, it was confirmed that the group consisting of fluorine which is a halogen acid needs to form apatite minerals such as calcium fluoride and calcium silicofluoride in the presence of a sufficient calcium component.

従来技術においては、改質対象素材に共存する有害元素群を不溶化処理し、同時に形状化処理するときに、不溶化処理ならびに形状化処理に必要な成分を系外から各種の改質処理剤に求めて添加配合して改質対象素材を改質してきた。本発明者等は、まず改質対象素材を構成する休眠成分を改質処理剤である遊離のイオン性ナトリウム成分により活性化し、ついで活性化された休眠成分の改質処理剤と配合量の管理されたナトリウム成分を活用してpH値が10未満で形成される水不溶性鉱物に共存有害元素群を固定化し、共存有害元素群を水不溶性に改質する条件を検討した。  In the prior art, when a group of harmful elements coexisting in the material to be modified is insolubilized and simultaneously shaped, the components required for insolubilization and shaping are obtained from various modification treatment agents from outside the system. The material to be modified has been modified by adding and blending. The present inventors first activate the dormant component constituting the material to be modified by the free ionic sodium component, which is the modifying treatment agent, and then control the treatment agent and the blending amount of the activated dormant component The conditions for modifying the coexisting harmful element group to be water-insoluble by immobilizing the coexisting harmful element group on the water-insoluble mineral formed at a pH value of less than 10 by using the sodium component was investigated.

しかし、廃棄物類を構成する不活性な休眠成分のシリカ、アルミナ、カルシヤ成分を活性化するためには、pH12以上の高いアルカリ性を示すナトリウム成分が必要であり、また一方有害金属類であり、オキソ酸を形成する鉛、クロム、ヒ素、セレン、ホウ素からなるグループ金属は、過剰なアルカリに容易に溶解する方向にあり、過剰なアルカリ共存下でこれら元素群を不溶化させることはできない。したがって、不活性な休眠成分を活性化せしめる条件とオキソ酸を形成して水溶出する有害金属類の不溶化条件を同一条件下で満足させることは拮抗しており困難であることを確認した。  However, in order to activate the inactive dormant components silica, alumina, and calcium components constituting the wastes, a sodium component exhibiting a high alkalinity of pH 12 or higher is necessary, while they are harmful metals. The group metal composed of lead, chromium, arsenic, selenium, and boron that forms oxo acid is easily dissolved in excess alkali, and these element groups cannot be insolubilized in the presence of excess alkali. Therefore, it was confirmed that satisfying the conditions for activating the inactive dormant component and the insolubilization conditions for toxic metals that form oxoacids and elute in water under the same conditions are difficult and difficult.

以上の確認条件により本発明者等は、不活性な休眠成分を活性化する条件とオキソ酸を形成する有害金属類の不溶化せしめる条件を同一条件下で満足させる改質技術を検討し、廃棄物類の休眠成分を活性化せしめるに必要なアルカリ成分は、休眠成分の活性化工程で充分に使い果たして、オキソ酸を形成する有害金属類を溶解するには不満足な条件とすると共に、有害元素群を一律に不溶化鉱物に形成せしめるに適切なアルカリ成分量をカルシヤ成分で確保できる改質処理剤による技術管理が重要と判断した。  Based on the above confirmation conditions, the present inventors have studied a reforming technique that satisfies the conditions for activating the inactive dormant component and the conditions for insolubilizing toxic acids that form oxo acids under the same conditions, and Alkaline components necessary to activate the dormant component of the class are used up in the activation process of the dormant component, making it an unsatisfactory condition for dissolving toxic acids that form oxo acids, Therefore, it was judged that it is important to manage the technology with a modification treatment agent that can secure an appropriate amount of alkali component with the calcium component in order to uniformly form insoluble minerals.

その結果本発明者等は、少なくとも常温における改質処理操作により、pH値で12以上の強いアルカリ性を示す改質処理剤を採択して、熱履歴シリケートからなる廃棄物類を構成している休眠成分のケイ酸塩化合物を予め活性化せしめて活用して、系内に有害物資として共存するアルカリ成分ならびに3グループに分類される有害元素群全てを水不溶性鉱物として固定化せしめる改質技術を見出し、しかも有害物資をpH値10未満で固定化形成せしめた水不溶性鉱物が、中性域の水系溶媒のみならず、酸性雨が想定される酸性域にあるpH4の溶液にさらしても、処理物に固定化されたアルカリ成分ならびに有害元素群を系外に溶出させない処理条件ならびに処理技術を見出した。  As a result, the present inventors have adopted a modification treatment agent exhibiting a strong alkalinity of 12 or more at a pH value by a modification treatment operation at least at room temperature, and constitute a dormancy comprising wastes composed of heat history silicate. We have discovered a modification technology that activates and uses the silicate compounds as components in advance to immobilize all of the alkaline components coexisting as harmful substances in the system and all the harmful elements classified into three groups as water-insoluble minerals. Moreover, even if the water-insoluble mineral in which harmful substances are fixed and formed at a pH value of less than 10 is exposed not only to a neutral aqueous solvent but also to a pH 4 solution in an acidic region where acid rain is assumed, The processing conditions and the processing technology that did not elute the alkali component and harmful element group immobilized on the system out of the system were found.

一方、本発明者等は、有害物資であるダイオキシン類は、油性であることから、水成分と接触するとその表面張力の差から、水成分雰囲気下では油分は集合して油滴化する傾向にあり、分解剤であるナトリウムイオンとの分子状での接触を不可能としていることから、油分性状を有するダイオキシン類を分子状に分散せしめるために、まずダイオキシン類を表面積が大きく親油性の高いケイ酸塩化合物表面で分子状に広げ、分解剤のナトリウムイオンと油性ダイオキシン類を分子状での接触を可能とするときは、ダイオキシン類を低温である常温でも分解して無害化処理できる改質処理条件を見出した。  On the other hand, since the dioxins, which are harmful substances, are oily, the inventors of the present invention tend to aggregate and form oil droplets in the water component atmosphere due to the difference in surface tension when in contact with the water component. In order to disperse the dioxins having oily properties in the molecular form, the dioxins having a large surface area and high lipophilicity are first used. When it is spread in the form of molecules on the surface of the acid salt compound and the sodium ion of the decomposing agent and the oily dioxins can be contacted in the form of molecules, it can be detoxified by decomposing the dioxins even at low temperatures. I found the condition.

なお、以上の少なくとも常温において有害物質類を無害化処理できる条件を見出した現象と条件は、同時に廃棄物類のケイ酸塩化合物である粉粒体をpH値12以上のアルカリを示す改質処理剤を作用させて、水中で再泥化しない耐水性の処理物に改質する形状化処理を可能にすることを見出した。この改質処理条件から、有害物質を共存する廃棄物類を低コストで環境に特別な負荷を与えることなく再生利用可能な無公害型の再資源化資材として提供でき、環境問題の解消に貢献できる効果を見出した。  In addition, the phenomenon and the condition which found the conditions which can detoxify the harmful substances at least at the above normal temperature and the conditions are the modification process which shows the alkali having a pH value of 12 or more at the same time for the granular material which is a silicate compound of wastes. It has been found that a shaping treatment can be made by modifying a water-resistant treated product that does not re-mudify in water by acting an agent. From these reforming treatment conditions, waste that coexists with hazardous substances can be provided as a non-polluting, recyclable material that can be recycled at a low cost without any special environmental impact, contributing to the resolution of environmental problems. I found a possible effect.

なお、本発明改質対象素材の廃棄物類は、ケイ酸塩系化合物を主成分として有害物質を共存する熱履歴を受けているシリケートであるが、本発明者等が見出した廃棄物類を改質対象素材とする改質処理技術は、有害物質を共存していない熱履歴シリケートであるケイ酸塩系化合物を改質対象素材として選び、ここに無害化処理ならびに形状化処理を施して、廃棄物類の再資源化資材である趣向資材、生活資材、工業用資材、建築・土木資材、自然環境資材ないし植物育成資材として提供できるが可能である。  In addition, although the wastes of the material subject to modification of the present invention are silicates that have received a thermal history of coexisting toxic substances with a silicate compound as the main component, the wastes found by the present inventors etc. The reforming treatment technology used as the material to be reformed is selected as a material to be reformed, a silicate compound that is a heat history silicate that does not coexist with harmful substances, and is subjected to detoxification treatment and shaping treatment. It can be provided as a material for recycling waste materials such as preference materials, living materials, industrial materials, construction / civil engineering materials, natural environment materials, or plant cultivation materials.

[本発明技術の概要]
以上、背景技術の項ならびに本発明に至った経過の項で詳述したように、本発明者等が本発明において見出した現象は、少なくとも常温で有害物質を共存する熱履歴シリケートを不溶化対象素材とする場合、特に有害元素群の内重金属類(カドミニウム、砒素、水銀、鉛、クロム、セレン)のみを不溶化対象元素とせず、アルカリ成分に充分可溶なホウ素ならびにフッ素を同様に一括して不溶化対象元素とし、常温において水を介したpH12以上にある改質処理剤を活用して、まず活性化混和物を調製する混和工程を経て、次いでこの活性化混和物を少なくとも常における養生工程に付する一連の改質方法により、改質対象素材と本発明改質処理剤の間で起こる反応により、pH値が10未満に確保された改質処理物を形成する作用機構原理は下記に示す現象にある。
[Outline of the present invention]
As described above in detail in the section of the background art and the section of the process leading to the present invention, the phenomenon found by the present inventors in the present invention is the material to be insolubilized by heat history silicate that coexists with harmful substances at least at room temperature. In particular, not only the heavy metals (cadmium, arsenic, mercury, lead, chromium, selenium) in the toxic element group are not targeted for insolubilization, but boron and fluorine, which are sufficiently soluble in alkali components, are similarly insolubilized together. Utilizing a modification treatment agent having a pH of 12 or more via water at room temperature as a target element, first, an admixture step for preparing an activated admixture is performed, and then this activated admixture is subjected to at least a normal curing step. By this series of reforming methods, a working mechanism that forms a reformed product having a pH value of less than 10 due to a reaction that occurs between the material to be reformed and the reforming agent of the present invention. Is in the phenomenon shown below.

即ち、少なくとも常温において改質対象素材と本発明改質処理剤の間で起こる現象は、
1.改質対象素材の休眠成分であるシリカやアルミナをpH12以上で活性化
2.低アルカリ性にある活性化成分で水不溶性鉱物に有害元素群を一括固定化
3.改質対象素材共存のダイオキシン類を分子状分散にて常温分解して無害化
4.粉粒体の改質対象素材を結着・硬化せしめて耐水性の水再泥化阻止形状化、
以上の4現象にあり、本発明技術において起こる現象の発生機構原理は、以下のように説明され、理解することができる。
That is, the phenomenon that occurs between the material to be modified and the present modification treatment agent at least at room temperature is
1. 1. Activate silica and alumina, which are dormant components of the material to be modified, at pH 12 or higher. 2. Immobilization of harmful elements on water-insoluble minerals with a low alkaline activation component. 3. Dioxins coexisting with the material to be modified are decomposed at room temperature by molecular dispersion to make them harmless. Water-resistant water re-mudging prevention shape by binding and curing the material to be modified powder,
There are the above four phenomena, and the principle of the mechanism of the phenomenon that occurs in the technology of the present invention can be explained and understood as follows.

1.改質対象素材に共存する水溶出する有害な金属群を固定化できる機構原理は、本発明改質処理剤のナトリウム成分が改質対象素材の休眠成分であったシリカ、アルミナ、カルシヤ等を活性化して消費され、しかも溶出するオキソ酸を形成する有害金属群や酸類元素を溶解せしめることのない範囲のナトリウム量に調整され、この時活性化されたシリカ、アルミナ、カルシヤ等を活用してアルミノケイ酸塩アルカリからなる水不溶性鉱物(ゼオライト・ゼオライト前駆体等)を形成し、この水不溶性鉱物に溶出有害金属群のイオンならびにナトリウムイオンが組み込まれ、溶出有害金属群ならびにナトリウム金属が水不溶性に固定化する現象に由来している。したがって、この現象により共存するアルカリ成分も固定化されることから、形成する結着形状体のpH値を10未満、好むらくは8.6以下の低アルカリ性で形成する現象を説明することができる。1. The mechanism principle that can fix the water-eluting harmful metal group coexisting in the material to be modified is that the sodium component of the present modification treatment agent activates silica, alumina, calcium, etc. that were dormant components of the material to be modified It is adjusted to a sodium amount in a range that does not dissolve the toxic metal group and acid elements that form the oxo acid that is consumed and dissolved, and activated at this time using activated silica, alumina, calcium, etc. Forms water-insoluble minerals (zeolites, zeolite precursors, etc.) consisting of alkali acid salts, and ions of the eluting hazardous metals and sodium ions are incorporated into the water-insoluble minerals, and the eluting hazardous metals and sodium metals are fixed in water-insoluble. It originates from the phenomenon that becomes. Therefore, since the coexisting alkali component is also fixed by this phenomenon, it is possible to explain the phenomenon that the formed binder is formed with a low alkalinity of a pH value of less than 10, preferably 8.6 or less. .

本発明において、以上の現象で重要なことは、改質対象素材の休眠成分を活性化するに必要なナトリウム成分の量、ならびにオキソ酸を形成して溶出する有害元素群や酸類元素を溶解するに必要なナトリウム成分の量とは、本発明の改質処理行為の上で拮抗しており、このナトリウム成分量の拮抗条件を充分に管理された内容で改質処理剤の成分を構成せしめ、活用する条件に本発明の特徴があり、重要なポイントである。  In the present invention, what is important in the above phenomenon is that the amount of sodium component necessary for activating the dormant component of the material to be modified, as well as the toxic element group and acid elements that elute by forming oxo acids are dissolved. The amount of the sodium component necessary for antagonizing on the modification treatment action of the present invention, the component of the modification treatment agent is configured with sufficiently controlled contention conditions for this sodium component amount, The conditions to be used have the characteristics of the present invention and are important points.

2.改質対象素材に共存するダイオキシン類を少なくとも常温で分解して無害化できる機構原理は、ダイオキシン類は油性成分であり、ダイオキシン類に対して分解機能を発揮できるナトリウムイオンは水性成分であり、本来油性成分と水性成分は、それぞれの界面張力の差から完全に二層に分離して一般には水性成分中に油滴となって共存する。したがって、水性系で分解能を有するナトリウムイオンと油性系のダイオキシン類との単純な混合・混和では、分解機能を有するアルカリ成分と油性のダイオキシン類とを分子状ないしはコロイド状に分散せしめて接触せしめることは不可能である。2. The mechanism principle that dioxins coexisting in the material to be reformed can be detoxified by decomposing at least at room temperature is that dioxins are oil-based components, and sodium ions that can exert a decomposition function on dioxins are aqueous components, The oily component and the aqueous component are completely separated into two layers from the difference in interfacial tension, and generally coexist as oil droplets in the aqueous component. Therefore, simple mixing / mixing of aqueous sodium ion with resolution and oil-based dioxins makes it possible to disperse the alkaline component having a decomposing function and oil-based dioxins in molecular or colloidal contact. Is impossible.

したがって、従来ダイオキシン類の分解機構は、1000℃付近の高温でダイオキシン類をガス状に広めて熱もしくは分解剤の接触により分解されてきた。本発明改質処理剤は、親油性のケイ酸塩類が構成成分として配合されることから、改質対象素材に油成分が共存する時は、その油成分は、改質対象素材ないし改質処理剤を構成している親油性ケイ酸塩類により、常温で油性ダイオキシン類を広いコロイド状微細粒子に広め、大きい表面積を有する分子状コロイドに乳化分散せしめ、分解能を有するアルカリ粒子との効率よい分子状での接触を可能とし、常温で無害化分解を可能とするところにある。  Therefore, the conventional decomposition mechanism of dioxins has been decomposed by spreading the dioxins in a gaseous state at a high temperature around 1000 ° C. by contact with heat or a decomposition agent. Since the present modification treatment agent is blended with lipophilic silicates as a constituent component, when the oil component coexists in the material to be reformed, the oil component is the material to be reformed or the reforming treatment. The lipophilic silicates that make up the agent spread the oily dioxins to a wide range of colloidal fine particles at room temperature, and then emulsify and disperse them in a molecular colloid with a large surface area. It can be contacted at a room temperature and can be detoxified at room temperature.

3.一方粉粒体の改質対象素材を結着・硬化せしめて一定強度を有する耐水性固化体に形状化できる機構原理は、ナトリウム成分の配合量が特定されている活性化活用成分の活用により、休眠成分であったシリカ、アルミナ、カルシヤ等を活性化して活性なシラノール基を伴う活性分を形成せしめ、本発明結着形状体の基本マトリックス骨格となる網目状シリカポリマーが生成する。次いでこの網目状シリカポリマーの隙間に、ケイ酸カルシウム系もしくは石こう系の水和鉱物ならびにアルミノケイ酸塩アルカリからなる水不溶性鉱物が沈着生成し、基本マトリックス骨格全体を耐水性で所定強度が確保された結着形状体に改質処理することが可能となる。3. On the other hand, the mechanism principle that can be formed into a water-resistant solidified body having a certain strength by binding and curing the material to be reformed powder, Silica, alumina, calcium, and the like, which are dormant components, are activated to form active components with active silanol groups, and a reticulated silica polymer that forms the basic matrix skeleton of the bound shape of the present invention is produced. Next, a water-insoluble mineral composed of calcium silicate or gypsum hydrated mineral and alkali aluminosilicate was deposited and formed in the gaps between the mesh silica polymers, and the entire basic matrix skeleton was water-resistant and predetermined strength was ensured. It becomes possible to perform a modification treatment on the bound shape.

以上示してきた本発明の改質処理技術においては、有害物質を共存している廃棄物類等の熱履歴を受けているシリケートを改質対象素材として、少なくとも常温で本発明技術を発揮させて調製した活性化混和物を形状化処理物を結着硬化せしめて原位置非成型物、耐水性粉粒体物ないしは形状加工成型物、また流動性活性化混和物を予め用意された応用対象基材に付着せしめて付着化処理物として応用付着調製して応用対象基材と一体化された結着成型活性物、基材積層複合物、顆粒群体集合物ないしは注充填一体化物からなるpH10未満が確保された結着形状体とすることができる。  In the reforming treatment technology of the present invention described above, the present technology can be demonstrated at least at room temperature, using a silicate that has received a heat history such as wastes coexisting with harmful substances as a material to be reformed. The prepared activated admixture is bonded and cured to the shaped processed product, and in-situ non-molded product, water-resistant granular material or shaped processed molded product, and fluidized activated admixture are prepared in advance. It has a pH of less than 10 consisting of a binder-molded active material, a base material laminated composite, a granule aggregate aggregate, or an injection-filled integrated material, which is attached to a material and applied as an adhesion-treated product and integrated with the base material to be applied. It can be set as the secured binding shape body.

本明細書で「常温」とは、自然条件の天候により生活環境で示される温度設定であり、一般には5ないしは40℃の範囲の温度をいうが、本発明技術に必要な温度範囲は常温に限定されるものではない。また、本明細書で「無害化処理」ならびに「形状化処理」とは、以下のように定義される。「無害化処理は」、少なくとも常温で加えたpHで12を超える改質処理剤を活用して、処理品のpH値を10未満に固定化し、共存する水溶出の有害な元素群を固定・不溶化して中性域のみならず酸性域(酸性雨を想定)における溶出試験においても有害な金属群の溶出が環境基準値の範囲内で不溶化され、ならびにダイオキシン類の含有量が毒性換算で環境基準値の範囲内に分解され無害化されている状態をいう。また「形状化処理」は、粉粒体の改質対象素材が低アルカリで耐水性が確保され水中で再泥化しない硬化・固化体に形状化されている状態をいう。  In the present specification, “normal temperature” is a temperature setting indicated in the living environment by natural weather conditions, and generally refers to a temperature in the range of 5 to 40 ° C., but the temperature range required for the technology of the present invention is normal temperature. It is not limited. In the present specification, “detoxification process” and “shaping process” are defined as follows. “Detoxification treatment” uses a modification treatment agent that exceeds 12 at a pH applied at room temperature to fix the pH value of the treated product to less than 10 to fix the coexisting elements of water-elution harmful elements. In the elution test not only in the neutral zone but also in the acidic zone (assuming acid rain), the elution of harmful metals is insolubilized within the range of the environmental standard value, and the dioxin content in the environment in terms of toxicity A state that is decomposed and detoxified within the standard value range. “Shaping treatment” refers to a state in which the material to be reformed of the granular material is shaped into a cured / solidified body that has low alkali and water resistance and is not re-mudged in water.

したがって、本明細書においては、本発明技術により重金属類を含む有害元素群の不溶化処理が中性水域のみならず酸性水域にさらされても環境汚染を防止できる実態を評価するため、下記に示す2種類の溶出試験法(後述する物性等の評価試験方法の項を参照)により、廃棄物類ならびに改質された再資源化資材における重金属類を含む有害元素群の溶出状況を下記に示す2種類の分析試験方法により評価した。  Therefore, in the present specification, in order to evaluate the actual situation in which environmental pollution can be prevented even if the insolubilization treatment of harmful elements including heavy metals is exposed to not only neutral water but also acidic water by the technology of the present invention, the following is shown. The elution status of hazardous elements including heavy metals in waste and modified recycled materials is shown below by two types of elution test methods (see the section of evaluation test methods for physical properties, etc. described later) 2 It was evaluated by various analytical test methods.

1.中性域における溶出試験:環境省46号溶出試験法
2.酸性域における溶出試験:オランダNEN7341溶出試験法
なお、酸性域における溶出試験であるオランダNEN7341溶出試験法は、自然界暴露における酸性雨を想定した状況下での評価方法であり、また、同時に本発明技術で酸域不溶化処理された活用品を自然界に暴露したときの促進試験として評価する。
1. 1. Dissolution test in neutral range: Ministry of the Environment 46 dissolution test method Dissolution test in the acidic region: Netherlands NEN7341 dissolution test method The dissolution test in the Netherlands NEN7341 which is a dissolution test in the acidic region is an evaluation method under the assumption of acid rain in exposure to nature. This product is evaluated as an accelerated test when a product that has been insolubilized with acid is exposed to nature.

[熱履歴シリケート]
本発明における改質対象素材は、熱履歴を受けているシリケートであるケイ酸塩化合物からなる粉粒体ないしは粉粒体に水を含んだ含水体を対象とする。本発明の熱履歴シリケートは、有害物質等を含まない人工合成品も改質対象素材とすることもできるが、一般的に人もしくは環境に悪影響を与えている有害物質を共存する熱履歴シリケートである廃棄物類を改質対象素材とするところに意味があり重要である。
[Heat history silicate]
The material to be modified in the present invention is a powder or hydrated body containing water in a silicate compound that is a silicate that has undergone a thermal history. The thermal history silicate of the present invention can be an artificial synthetic product that does not contain harmful substances or the like, and can be used as a material to be modified, but is generally a thermal history silicate that coexists with harmful substances that adversely affect people or the environment. It is meaningful and important to use certain waste as a material to be modified.

廃棄物類は、廃棄物の処理及び清掃に関する法律(廃掃法)において「ごみ、粗大ごみ、燃え殻、汚泥、ふん尿、廃油、廃酸、廃アルカリ、動物の死体その他の汚物または不要物であって、放射性物質およびこれによって汚染されたものを除く固形状または液状のもの」と定義されている。本発明の廃棄物類では、ケイ酸塩系化合物を主成分とする熱履歴シリケートを改質対象素材としている。  Wastes are classified as “garbage, oversized waste, burning husk, sludge, manure, waste oil, waste oil, waste acid, waste alkali, animal carcasses and other filth or unnecessary waste in the law on waste disposal and cleaning (Waste Removal Law). , Solid or liquid excluding radioactive substances and those contaminated thereby ". In the wastes of the present invention, a heat history silicate mainly composed of a silicate compound is used as a material to be modified.

本発明改質対象素材に採択される熱履歴を受けているシリケートとしては、乾燥物による酸化物基準で表してシリカ成分を24ないし80質量%、アルミナ成分を6ないし45質量%、カルシヤ成分を4ないし65質量%を主成分として、選択によってはナトリウム成分を10質量%以下の量を主成分とする混合原料が820ないし1800℃で熱処理を受けているケイ酸塩系化合物を主成分とするシリケートを総称している。  The silicate that has been subjected to the thermal history adopted as the material to be modified according to the present invention is represented by 24 to 80% by mass of the silica component, 6 to 45% by mass of the alumina component, and 6 to 45% by mass of the alumina component. A mixed raw material containing 4 to 65 mass% as a main component and, depending on selection, a sodium component as a main component in an amount of 10 mass% or less is mainly composed of a silicate compound that has been heat-treated at 820 to 1800 ° C. It is a general term for silicates.

したがって、本発明の熱履歴シリケートは、非晶質またはガラス質の化合物ないしは組成物等で構成される不活性な休眠成分からなるケイ酸塩化合物主成分としており、この不活性な休眠成分の好適な粒径は500μ以下の範囲にある微粒子に粉砕・分級されているシリケートからなる粉粒体が好ましい。  Therefore, the heat history silicate of the present invention has a silicate compound main component composed of an inactive dormant component composed of an amorphous or glassy compound or composition, etc., and is suitable for this inactive dormant component. A granular material made of silicate that is pulverized and classified into fine particles having a fine particle size in the range of 500 μm or less is preferable.

また本発明における改質処理工程では、改質対象素材と本発明改質処理剤と2者を一旦して水を介した活性化混和物に形成せしめる混和工程が必須であることから、本発明で処理対象とする素材には、既に本発明の水系溶媒が包含担持された含水体で構成されることも構わない。このときの粉粒体からなる改質対象素材の乾燥物基準で100質量部に対して水が120質量部以下の量割合で包含担持されている含水体を好適に挙げることができる。  In addition, in the modification treatment step of the present invention, the mixing step of forming the material to be modified, the modification treatment agent of the present invention and the two into an activated admixture through water is essential. The material to be treated in (1) may be composed of a hydrous material that already contains and supports the aqueous solvent of the present invention. A water-containing body in which water is included and supported in an amount ratio of 120 parts by mass or less with respect to 100 parts by mass on the basis of the dry matter of the material to be reformed composed of the granular material at this time can be preferably exemplified.

人工合成品
本発明における人工合成品からなる熱履歴シリケートは、予め調製される混合原料をケイ酸塩組成物、カルシヤ組成物ならびにアルミナ組成物の群より選ばれる単独ないし2種以上の組み合わせからなる混合原料で構成されており、該混合原料が主成分として乾燥物の酸化物基準で表してシリカ100質量部に対して、カルシヤ30ないし350質量部ならびにアルミナを10ないし150質量部、必要に応じて酸化ナトリウムを1ないし50質量部の範囲で構成されており、該混合原料を820ないし1500℃の範囲で少なくとも15分間熱処理し、次いで回収された熱処理物を80メッシュ、好むらくは150メッシュ篩通過の微粒子に粉砕・分級して調製することができる。
Artificial synthetic product The heat history silicate comprising the artificial synthetic product of the present invention is composed of a single raw material or a combination of two or more selected from the group consisting of a silicate composition, a calcium composition and an alumina composition. It is composed of a mixed raw material, and the mixed raw material is expressed in terms of oxides of the dried product as a main component, with respect to 100 parts by mass of silica, 30 to 350 parts by mass of alumina and 10 to 150 parts by mass of alumina as necessary. The mixed raw material is heat treated at a temperature of 820 to 1500 ° C. for at least 15 minutes, and then the recovered heat treated product is 80 mesh, preferably 150 mesh sieve. It can be prepared by pulverizing and classifying the fine particles.

本発明の人工合成品を調製する混合原料のケイ酸塩組成物は、酸化物基準で表して少なくともシリカを45ないし80質量%、アルミナを5ないし35質量%、アルカリ土金属の酸化物を0.5ないし25質量%含有する層状粘土鉱物、シリケート、含水土質類、熱履歴シリケートもしくは廃ケイ酸塩類の群により選ばれる単独ないし2種以上の組み合わせのケイ酸塩化合物を選ぶことができる。  The mixed silicate composition for preparing the artificial synthetic product of the present invention has at least 45 to 80% by weight of silica, 5 to 35% by weight of alumina, and 0 to 0% of an alkaline earth metal oxide on an oxide basis. It is possible to select a single or a combination of two or more silicate compounds selected from the group consisting of layered clay minerals, silicates, hydrous soils, thermal history silicates or waste silicates containing 5 to 25% by mass.

熱履歴シリケートの人工合成品の混合原料
混合原料を構成するケイ酸塩組成物である層状粘土鉱物は、アロフェン、ヒシンゲル石、パイロフェライト、タルク、雲母、モンモリロナイト石群、バーミキュル石、リョクデイ石群、カオリナイトもしくはイノケイ酸塩の群より選ばれる単独ないし2種以上の組み合わせのフェロケイ酸塩を好適に挙げることができる。
Mixed raw material of artificial synthetic product of heat history silicate Layered clay mineral, which is a silicate composition that constitutes the mixed raw material, is allophane, hysinger gel, pyroferrite, talc, mica, montmorillonite stone group, vermiculite, ryokdeite group, Preferable examples include single or a combination of two or more ferrosilicates selected from the group of kaolinite or inosilicate.

混合原料を構成するケイ酸塩組成物であるシリケートは、天然または合成のケイ酸塩化合物でウオラストナイト、ゾーノトライトやトバモライトであるケイ酸カルシウムやケイ酸マグネシウム、ケイ石、石英、珪藻土、長石類、沸石、花崗岩・変成岩・流紋岩・礫岩等の岩石鉱物、モルデン石からなるアルミノケイ酸塩鉱物もしくは水ガラスやガラス類のケイ酸アルカリの群から選ばれる単独ないし2種以上の組み合わせのケイ酸塩化合物を好適に挙げることができる。  Silicate, a silicate composition that constitutes the mixed raw material, is a natural or synthetic silicate compound, wollastonite, zonotolite and tobermorite, calcium silicate, magnesium silicate, quartzite, quartz, diatomaceous earth, feldspar , Zeolite, granite, metamorphic rock, rhyolite, conglomerate and other rock minerals, aluminosilicate minerals composed of mordenite, or a single or a combination of two or more selected from the group of water glass and glass alkali silicates Preferable examples include acid salt compounds.

混合原料を構成するケイ酸塩組成物である含水土質類は、水分を少なくとも25質量%含有する建設工事現場地盤や副生土、海・湖・沼・河川・ダムに堆積している底質、含水粘土質土壌、泥状泥土、有機質土、岩石の風化土、軟弱地盤土壌、砂質土もしくは下水汚泥の群より選ばれる単独ないし2種以上の組み合わせの含水土質類であるケイ酸塩化合物を好適に挙げることができる。  Hydrous soils, which are silicate compositions that make up mixed raw materials, are sediments on the construction site ground and by-product soil that contain at least 25% by weight of moisture, and sediments deposited on the sea, lakes, swamps, rivers, and dams. Silicate compound which is a single or a combination of two or more hydrous soils selected from the group consisting of hydrous clay soil, mud mud soil, organic soil, rock weathered soil, soft ground soil, sandy soil or sewage sludge Can be preferably mentioned.

混合原料を構成するケイ酸塩組成物である熱履歴シリケートは、ケイ酸塩を主成分とする廃棄物類もしくは下水汚泥の焼却灰、乾留処理灰、フライアッシュ、高炉や製鋼スラグ、火山灰や溶岩の火山噴出物、窯業廃材もしくはケイ酸塩系ガラス類の群より選ばれる単独ないし2種以上の組み合わせの熱履歴のあるシリケート類であるケイ酸塩化合物を好適に挙げることができる。  Thermal history silicate, which is a silicate composition that constitutes the mixed raw material, is incinerated ash, dry distillation ash, fly ash, blast furnace, steelmaking slag, volcanic ash and lava. Preferred examples include silicate compounds that are silicates having a thermal history of a single or a combination of two or more selected from the group of volcanic products, ceramic wastes, and silicate glasses.

混合原料を構成するケイ酸塩組成物である廃ケイ酸塩物は、酸化物基準で表してシリカ含有量が20質量%以上である油分含有の廃白土、上水・下水処理排出ならびに農業集落排水の汚泥ケーキ、窯業関連廃品・廃材、保温・断熱・耐熱・耐火材の廃材、建設・土木業界の残土・廃土、ガラスカレット・廃ガラス屑もしくは製造業界から排出されるケイ酸塩系廃棄物類の群より選ばれる単独ないし2種以上の組み合わせのケイ酸塩系廃棄物を好適に挙げることができる。  Waste silicate, which is a silicate composition that constitutes a mixed raw material, is an oil-containing waste white clay having a silica content of 20% by mass or more in terms of oxides, water and sewage treatment discharges, and agricultural settlements. Sludge cake for wastewater, ceramics-related wastes / waste materials, heat insulation / heat insulation / heat resistant / refractory waste materials, residual soil / waste soil in the construction / civil engineering industry, glass cullet / waste glass waste or silicate waste discharged from the manufacturing industry A single or a combination of two or more silicate wastes selected from the group of substances can be preferably mentioned.

本発明の人工合成品の調製する混合原料のカルシヤ組成物は、カルシヤを少なくとも20質量%以上含有するカルシウム塩組成物、廃棄物類組成物、カルシヤ含有鉱物組成物および炭カル変性組成物の群より選ばれる単独ないし2種以上の組み合わせのカルシウム塩化合物を選ぶことができる。  The mixed raw material calcium composition prepared by the artificial synthetic product of the present invention is a group of calcium salt composition, waste composition, calcium-containing mineral composition and charcoal cal-modified composition containing at least 20% by mass of calcium. A single calcium salt compound or a combination of two or more selected calcium salt compounds can be selected.

混合原料を構成するカルシヤ組成物であるカルシウム塩組成物は、下記組成式(2)

Figure 2006247645
[式中;Tはアルミニウム、ケイ素、窒素、硫黄、炭素、ホウ素、リン元素群の単独ないし2種以上の組み合わせ元素、Xはハロゲン元素、a、b、cは零を含む10以下の数、mは0.5ないし6の数、wは零を含む28以下の数]で表されるカルシウムのオキシ酸塩もしくはハロゲン塩化合物の群より選ばれる単独ないし2種以上の組み合わせの正塩、塩基性塩、酸性塩もしくは酸化性塩のカルシウム塩化合物を好適に挙げることができる。The calcium salt composition which is a calcium composition constituting the mixed raw material has the following composition formula (2):
Figure 2006247645
[Wherein, T is an aluminum, silicon, nitrogen, sulfur, carbon, boron, phosphorus element group alone or a combination of two or more elements, X is a halogen element, a, b, c are 10 or less numbers including zero, m is a number of 0.5 to 6, w is a number of 28 or less including zero], or a normal salt or a base selected from the group of calcium oxyacid salts or halogen salt compounds A calcium salt compound of an acidic salt, acidic salt or oxidizing salt can be preferably mentioned.

混合原料を構成するカルシヤ組成物である廃棄物類組成物は、カルシヤを少なくとも20質量%含有する石灰中和スラッジ、廃石こう、副生石こう、高炉・製鋼スラグである鉱滓類、焼却場廃ガス中和用石灰ならびに廃ケイ酸カルシウムの群より選ばれる単独ないし2種以上の組み合わせのカルシウム塩系廃棄物を好適に挙げることができる。  Waste composition, which is a calcite composition constituting the mixed raw material, includes lime neutralized sludge containing at least 20% by weight of calcite, waste gypsum, byproduct gypsum, blast furnace / steel slag slag, incineration waste gas A calcium salt-based waste of a single or a combination of two or more selected from the group of neutralizing lime and waste calcium silicate can be preferably mentioned.

混合原料を構成するカルシヤ組成物であるカルシヤ含有鉱物組成物は、ポルトランドセメント、混合セメント、特殊セメント(アルミナセメント、超速硬性セメント、コロイド状セメント、油井セメント、地熱セメント、膨潤セメント)、炭酸ケイ素カルシウム、アルミン酸カルシウム、硫酸カルシウム、リン酸カルシウム、ケイ酸カルシウムの群より選ばれる単独ないし2種以上の組み合わせのカルシヤ含有鉱物類を好適に挙げることができる。  Calcium-containing mineral composition, which is the calcite composition constituting the mixed raw material, is Portland cement, mixed cement, special cement (alumina cement, super-hard cement, colloidal cement, oil well cement, geothermal cement, swelling cement), calcium calcium carbonate Preferred examples include calcium-containing minerals selected from the group consisting of calcium aluminate, calcium sulfate, calcium phosphate and calcium silicate alone or in combination of two or more.

混合原料を構成するカルシヤ組成物である炭カル変性組成物が、炭酸カルシウムを主成分とするカルシウム塩化合物100質量部に対して、塩酸、硫酸、亜硫酸、硝酸、亜硝酸、ケイ酸、アルミノケイ酸、アルミン酸、ホウ酸ならびにリン酸の群より選ばれる単独ないし2種以上の組み合わせの酸根を50質量部加えて、980℃以上で熱処理して脱炭酸されている炭カル変性組成物を好適に挙げることができる。  Charcoal cal-modifying composition, which is a calcium composition constituting the mixed raw material, is hydrochloric acid, sulfuric acid, sulfurous acid, nitric acid, nitrous acid, silicic acid, aluminosilicic acid with respect to 100 parts by mass of calcium salt compound mainly composed of calcium carbonate. A carbonic cal-modified composition that is decarboxylated by adding 50 parts by mass of an acid radical selected from the group consisting of aluminate, boric acid and phosphoric acid and heat-treating at 980 ° C. or higher is suitable. Can be mentioned.

本発明の人工合成品の調製する混合原料のアルミナ組成物は、下記組成式(3)

Figure 2006247645
[式中:Mはアルカリ金属、Zはアルカリ土類金属、aは零を含む5以下の数、bは零を含む5以下の数、wは零を含む9以下の数]で表されるアルカリ金属またはアルカリ土類金属のアルミン酸塩もしくはアルミナ水和物の群より選ばれる単独ないし2種以上の組み合わせのアルミニウム化合物を選ぶことができる。The alumina composition of the mixed raw material prepared by the artificial synthetic product of the present invention has the following composition formula (3)
Figure 2006247645
[Wherein, M is an alkali metal, Z is an alkaline earth metal, a is a number of 5 or less including zero, b is a number of 5 or less including zero, and w is a number of 9 or less including zero] Single or a combination of two or more aluminum compounds selected from the group of alkali metal or alkaline earth metal aluminate or alumina hydrate can be selected.

本発明の熱履歴シリケートは、原位置または持込位置に存在して、一般に有害物質を共存しているケイ酸塩系化合物を少なくとも50質量%含有しており、有害化学物質が環境基準値を超える範囲で共存している有機質素材類の乾留灰、石炭灰、ゴミや汚泥の焼却灰類、窯業系の土質廃棄物類、高炉・製鋼のスラグ類、汚泥・底質・脱水ケーキの含水泥土類、土壌・粘土・地盤類、生活・工業・土木資材類ないしは火山噴出物からなる群より選ばれる単独ないし2種以上の組み合わせの粉粒体ないしは含水体を廃棄物類の処理の立場からも好適に選ぶことができる。  The thermal history silicate of the present invention contains at least 50% by mass of a silicate compound that exists in the original position or in the carry-in position and generally coexists with harmful substances, and the harmful chemical substances have an environmental standard value. Organic materials co-existing in the range of dry distillation ash, coal ash, incineration ash of garbage and sludge, ceramic waste, blast furnace / steel slag, sludge, bottom sediment, dehydrated cake hydrous mud From the group of soil, clay, ground, life, industry, civil engineering materials, or volcanic ejecta alone or in combination of two or more types of powder or water It can choose suitably.

これら本発明改質対象素材になる熱履歴シリケートの具体的な例としては、改質対象素材が存在する原位置もしくは持込位置のいずれの場所に存在していても、熱履歴シリケートのケイ酸塩系化合物を少なくとも50質量%含有しており、有害物質が環境基準値を超える範囲で共存している人工合成品、有機質素材類の乾留灰・石炭灰・ゴミや汚泥の焼却灰類、窯業系の土質廃棄物類、高炉・製鋼のスラグ類、汚泥・底質・脱水ケーキを含む含水泥土類、土壌・粘土・地盤類、生活・工業・土木資材類ないしは火山噴出物からなる群より選ばれる単独ないし2種以上の組み合わせの粉粒体または含水体を好適に挙げることができる。なお、本発明技術で改質対象とする改質対象素材は、有害物質が環境基準値を超える範囲で共存する改質対象素材に限定されるものではない。  As specific examples of the heat history silicate that is the material to be modified according to the present invention, the silicic acid of the heat history silicate can be used regardless of whether the material to be reformed exists in the original position or the carry-in position. Artificial synthetic products containing at least 50% by mass of salt-based compounds, and harmful substances coexist in the range exceeding the environmental standard value, incinerated ash of organic materials such as carbonized ash, coal ash, garbage and sludge, ceramics Selected from the group consisting of sewage waste, blast furnace / steel slag, hydrous mud including sludge / sediment / dehydrated cake, soil / clay / ground, living / industrial / civil engineering materials or volcanic products Preferred examples thereof include a single granular material or a combination of two or more types of granular materials or water-containing materials. It should be noted that the material to be reformed that is the material to be reformed in the technology of the present invention is not limited to the material to be reformed in which harmful substances coexist in the range exceeding the environmental standard value.

これらの廃棄物類は、粉粒状、ガラクタ状、不特定形状、特定形状ないし含水状等の性状状態で排出されている。本発明改質対象素材に好適な性状状態は、取り扱い上、粉粒体ないしはこの粉粒体が含水している含水体であることが好ましい。しかし、廃棄物類の中にあっては、一般廃棄物・産業廃棄物類自身であって粉砕・分級ないしは一次的に各種手段で改質もしくは処理された粉粒体、顆粒体、成形体ならびに廃棄物類・放射性廃棄物等のガラクタ(板状、紐状、塊状、成型体状、アーモンド状、フレー状、砂状、粉状、ガラクタ状等)の集合体、一般廃棄物・産業廃棄物類を焼却または乾留した焼却灰類の燃え殻等があるが、これら各形状の廃棄物類も目的・用途に応じてそれぞれ採択することは可能である。  These wastes are discharged in a state of properties such as powder, gargle, unspecified shape, specified shape or water-containing shape. The property state suitable for the material to be modified according to the present invention is preferably a granular material or a hydrated body containing this granular material in handling. However, among the wastes, it is general wastes / industrial wastes themselves, which are pulverized, classified or primarily modified or treated by various means, granules, molded products, Aggregates of waste and radioactive waste (plate, string, lump, molded, almond, flare, sand, powder, trash, etc.), general waste / industrial waste Incineration ash obtained from incineration or dry distillation of incineration ash, etc., these types of waste can be selected according to the purpose and application.

勿論、これらの他の性状にある廃棄物類は、予め粉粒体ないしは含水体に精製・改質されて採択することもできる。また、これらの廃棄物類は各種の狭雑物等を混在していることが多いが、これらの狭雑物等は予め除去しておくことが好ましい。また、本発明における改質対象素材において、含水体を改質対象素材とするときは、含水体の含有水分量が含水比で150より大きいときは、必要に応じて含水比を150未満に脱水処理する前処理工程に付することが改質方法を有効に進める上で好ましい。  Of course, wastes having these other properties can be adopted after being refined and modified into powder or water-containing material in advance. In addition, these wastes often contain various kinds of contaminants, but it is preferable to remove these contaminants in advance. Further, in the material to be modified in the present invention, when the water-containing body is the material to be reformed, if the water content of the water-containing body is larger than 150 in the water content ratio, the water content is dehydrated to less than 150 as necessary. It is preferable to apply the pretreatment step for treatment in order to effectively advance the modification method.

また、本発明の改質対象素材となる他の熱履歴を受けているシリケートとしては、廃棄物類以外で火山噴出物である火山灰や溶岩等、窯業資材である耐熱材・断熱材・保温材等、工業用資材である建材・土木資材・植物育成資材・客土等を挙げることができる。これらの熱履歴シリケートガラは、有害物質類を共存していない場合もあるが、本発明の改質対象素材として本発明の改質処理剤改質方法を採択して、本発明の耐水性の結着形状体に改質して有効資材として提供することもできる。  In addition, as silicates that have undergone other thermal histories that become the material to be modified according to the present invention, heat-resistant materials, heat-insulating materials, and heat-insulating materials that are ceramic materials such as volcanic ash and lava other than wastes Examples of such materials are industrial materials such as building materials, civil engineering materials, plant cultivation materials, and soils. These heat history silicate glass may not coexist with harmful substances, but adopting the modification treatment method modification method of the present invention as a modification target material of the present invention, the water resistance of the present invention. It can also be provided as an effective material after being modified into a bound shape.

生成時期
したがって、本発明改質対象素材に採択されるシリケートが熱履歴を受けた時期は特に限定されるものではなく、例えば地球における自然界で発生した熱で過去に熱履歴を受けている場合、また地球における歴史的火山活動の産物であるシリケート、もしくは火山活動の産物が地殻の表面や地殻中もしくは海域中で堆積変化・風化したシリケートでもよく、その生成起原ならびに時期に特に限定されるものではない。
Therefore, the time when the silicate adopted as the material to be modified according to the present invention has received a heat history is not particularly limited, for example, when the heat generated in the natural world on the earth has received a heat history in the past, Also, silicates that are the products of historical volcanic activity on the earth, or silicates whose volcanic products were deposited and weathered in the surface of the crust, in the crust, or in the sea, and are limited to their origin and timing is not.

一般的に廃棄物類は、有害物質として重金属類等の元素群、ダイオキシン類、窒素(アンモニヤ態窒素、硝酸態)成分またはイオン性アルカリ(ナトリム・カルシウム・マグネシウム)成分等を共存しており、これらの有害物質は、廃棄物類より溶出・拡散して生活環境を汚染し、人や動植物に悪影響を与えている。  Generally, wastes coexist with elements such as heavy metals, dioxins, nitrogen (ammonia nitrogen, nitrate) components or ionic alkali (natrim / calcium / magnesium) components as harmful substances, These harmful substances are eluted and diffused from wastes, contaminating the living environment, and adversely affecting people, animals and plants.

本発明の熱履歴シリケートからなる改質対象素材に共存する有害物質は、先の背景技術の項で一部述べたが、環境省が「土壌・地下水汚染に係る調査・対策指針」で示している有害な元素群(カドミニウム、砒素、水銀、鉛、クロム、セレン、ホウ素、フッ素)、ダイオキシン類、窒素(アンモニヤ態窒素、硝酸態)成分またはイオン性アルカリ(ナトリム・カルシウム・マグネシウム)成分等を対象とする。なお、有害な元素群の各媒体類に対する汚染は、環境省より提示されている環境基準に示される土壌の溶出基準、地下水の含有基準、土壌含有参考値を参考に表1に示す。  Hazardous substances that coexist in the material to be reformed consisting of the heat history silicate of the present invention are partly described in the background section above, but the Ministry of the Environment indicated in the “Survey and Countermeasure Guidelines for Soil and Groundwater Contamination”. Harmful elements (cadmium, arsenic, mercury, lead, chromium, selenium, boron, fluorine), dioxins, nitrogen (ammonia nitrogen, nitrate) components or ionic alkali (natrim, calcium, magnesium) components, etc. set to target. Contamination of harmful elements to each medium is shown in Table 1 with reference to soil elution standards, groundwater content standards, and soil content reference values indicated in the environmental standards presented by the Ministry of the Environment.

Figure 2006247645
Figure 2006247645

またダイオキシン類による各媒体類に対する汚染は、環境省より提示されている環境基準を表2に示す。なお、本発明で処理対象となるダイオキシン類は、一般に油性性状を有する75種類の異性体を持つポリ塩化ジベンゾパラジオキシン(以下「PCDD」と略記)、ならびに135種類の異性体を持つポリ塩化ジベンゾフラン(以下「PCDF」と略記)、さらにコプラナーPCB(以下「PCB」と略記)を総称している。  Table 2 shows the environmental standards presented by the Ministry of the Environment for contamination of various media by dioxins. The dioxins to be treated in the present invention are generally polychlorinated dibenzopararadixins (hereinafter abbreviated as “PCDD”) having 75 isomers having oily properties, and polychlorinated dibenzofurans having 135 isomers. (Hereinafter abbreviated as “PCDF”) and coplanar PCB (hereinafter abbreviated as “PCB”).

なお、本発明改質処理剤による無害化処理とは、共存ダイオキン類の場合、ダイオキン類において化学的有機質骨格に結合している塩素が有機質骨格より外れて化学的に分解したことにより、ダイオキシン類の濃度が毒性効果を評価する換算係数を掛けて表したng−TEQ/gで評価して、環境基準値以下に消滅して毒性のない化合物に変化している状態をいう。ダイオキシン類のng−TEQ/g環境基準値を表2に示す。  Incidentally, the detoxification treatment with the present modification treatment agent means that in the case of coexisting dioxins, the dioxins are chemically decomposed by the fact that the chlorine bonded to the chemical organic skeleton is separated from the organic skeleton and chemically decomposed. This is a state in which the concentration of γ is evaluated by ng-TEQ / g expressed by multiplying a conversion factor for evaluating the toxic effect, and disappears below the environmental standard value and is changed to a non-toxic compound. Table 2 shows ng-TEQ / g environmental standard values of dioxins.

Figure 2006247645
Figure 2006247645

また、窒素成分の場合、水産用水規準の範囲内であり、アルカリ成分の場合、pHが10未満、好むらくは8.6以下の状態が確保され、生活環境で直接もしくは間接的に人の健康と生活に影響を及ぼさない安全な環境にある状態をいう。但し、本発明で窒素成分(アンモニヤ態窒素、硝酸態窒素、硝酸態窒素等)の有害規準は、全窒素成分で表示し、日本水産資源保護協会が「水産用水規準」の海域における望ましい溶出規準(水産3種)の全窒素濃度=1mg/Lを超える濃度を有害規準とした。  In the case of nitrogen component, it is within the range of water standards for fisheries, and in the case of alkaline component, pH is less than 10, preferably 8.6 or less, and human health is directly or indirectly secured in the living environment. It means a state in a safe environment that does not affect life. However, in the present invention, harmful standards for nitrogen components (ammonia nitrogen, nitrate nitrogen, nitrate nitrogen, etc.) are expressed as total nitrogen components, and the Japan Water Resources Conservation Association recommends the desirable elution standards for sea areas. The total nitrogen concentration of (Fisheries 3) = concentration exceeding 1 mg / L was defined as a harmful standard.

本発明で改質対象素材と改質処理剤からなる活性化混和物における常温3時間放置以内におけるpH値が12を超える状態にある確認は、混和物5gを100ccの純水に30分間分散溶解せしめた時のpH値の測定により評価した。なお、本発明の結着形状体におけるpH値の測定も同様にして評価した。ここで評価するpH値の評価基準を環境ならびに生物系に多大の悪影響を及ぼす危険性のない10未満とし、さらに好適には水道水規準値であるpHが8.6以下を基準として評価した。  In the present invention, the activated mixture composed of the material to be modified and the modification treatment agent is confirmed to have a pH value exceeding 12 within 3 hours at room temperature. Disperse and dissolve 5 g of the mixture in 100 cc of pure water for 30 minutes. Evaluation was made by measuring the pH value when caulking. In addition, the measurement of the pH value in the binding shape body of the present invention was similarly evaluated. The evaluation standard of the pH value evaluated here was set to less than 10 which has no risk of having a great adverse effect on the environment and biological system, and more preferably, the standard value of tap water was 8.6 or less.

本発明明細書では、特記しない限り、有害な元素群、ダイオキシン類、窒素(アンモニヤ態窒素、硝酸態窒素等)成分ないしは水可溶性のナトリウム成分やカルシウム成分群の単独ないし複数の有害物質を単に「有害物質」として表現記載することがある。なお、本明細書では、有害な元素群はイオン性のフッ素・ホウ素に重金属類を含めて総称しており、ダイオキシン類の毒性ダイオキシン類を「DXN」と略記することがある。  In the present specification, unless otherwise specified, harmful element groups, dioxins, nitrogen (ammonia nitrogen, nitrate nitrogen, etc.) components or water-soluble sodium components or calcium component groups alone or a plurality of harmful substances are simply “ Sometimes referred to as “toxic substances”. In the present specification, the harmful element group is a generic term including ionic fluorine / boron including heavy metals, and toxic dioxins of dioxins may be abbreviated as “DXN”.

[水系溶媒]
本発明の改質処理剤が有する作用機能を起動させる「水系溶媒」の介在が重要である。本発明の水系溶媒は、自然水[雨水、河川・湖沼水・たまり水、湧き水、井戸水、海水、人工池・ダム水等]、人工水[飲料水、工場用水、農業用水、水道水、下水道処理水、産業界の副生水、産業界の排水、生活排水、排水類の処理水等]、改質対象素材[含水土質、底質、土壌地盤、産業廃棄物類等]の含水ないしアルカリソルト溶液の群より選ばれる単独ないし2種以上の組み合わせ水系液体を好適に挙げることができる。
[Aqueous solvent]
It is important to intervene with an “aqueous solvent” that activates the function of the modifying treatment agent of the present invention. The water-based solvent of the present invention includes natural water [rain water, river / lake water / pool water, spring water, well water, seawater, artificial pond / dam water, etc.], artificial water [drinking water, industrial water, agricultural water, tap water, sewerage] Treated water, industrial by-product water, industrial wastewater, domestic wastewater, treated wastewater, etc.], water content or alkali of the material to be modified [hydrous soil, sediment, soil ground, industrial waste, etc.] A single or two or more combined aqueous liquids selected from the group of salt solutions can be preferably mentioned.

本発明水系溶媒は、本発明改質対象素材類ないし改質処理剤が既に水分を保持しているとき、例えば含水土質、底質、土壌地盤、アルカリソルト溶液等においては、改質対象素材や改質処理剤が含有する水分を本発明水系溶媒として活用することは有効であり、特別に水系溶媒を添加補給する必要はない。一般的な本発明水系溶媒は、入手が容易な自然水が好適であり、入手容易な水を海・河川・湖沼等から採取した水を好適に選ぶことができる。勿論、本発明の改質処理剤ならびに改質処理方法における水系溶媒として海水を採択しても、本発明改質処理剤の作用機構を損なうものでない。  The aqueous solvent of the present invention is used when the material to be modified or the treatment agent of the present invention already retains moisture, for example, in hydrous soil, sediment, soil ground, alkali salt solution, etc. It is effective to use the water contained in the modifying treatment agent as the aqueous solvent of the present invention, and it is not necessary to add and replenish the aqueous solvent. As the general aqueous solvent of the present invention, natural water that is easily available is suitable, and water obtained from the sea, rivers, lakes and the like can be suitably selected. Of course, even when seawater is adopted as the aqueous solvent in the modification treatment agent and the modification treatment method of the present invention, the working mechanism of the modification treatment agent of the present invention is not impaired.

[改質処理剤]
本発明技術は、熱履歴を受けて不活性な休眠成分であるケイ酸塩化合物を主成分とするシリケートを改質対象素材としている。したがって該改質対象素材に対して水を介して活性化機能を有する改質処理剤を加える一連の作業工程からなる少なくとも常温における改質方法を付することにより、該改質対象素材に無害化処理ならびに形状化処理が施されて無公害型で耐水性の結着形状体に改質処理する技術である。
[Modifying agent]
The technology of the present invention uses, as a material to be reformed, a silicate containing a silicate compound, which is an inactive dormant component under heat history, as a main component. Therefore, the material to be reformed is rendered harmless by applying a reforming method at least at room temperature comprising a series of work steps in which a reforming agent having an activation function is added to the material to be reformed through water. This is a technology for performing a modification treatment into a pollution-free and water-resistant binding shape body by performing the treatment and the shaping treatment.

したがって、本発明技術における目的においては、有害物質を共存する廃棄物類からなる改質対象素材を処理対象にして無害化処理ならびに形状化処理を可能とするシリカ、アルミナ成分、カルシヤ成分ならびに酸化ナトリウム成分は、系外から添加配合するのでなく、処理対象とする素材が保有する不活性な休眠成分のケイ酸塩化合物に求め、その休眠成分を構成するシリカ、アルミナ成分、カルシヤ成分ならびに酸化ナトリウム成分を活性化して活用するところに本発明の特徴がある。したがって、休眠成分を活性化できる機能性を効率よく有効に少なくとも常温で発揮して、無害化処理ならびに形状化処理を可能せしめる改質処理剤の役割は重要である。  Therefore, for the purpose of the technology of the present invention, silica, alumina component, calcium component, and sodium oxide that enable detoxification treatment and shaping treatment on a material to be modified consisting of wastes that coexist with harmful substances can be treated. Ingredients are not added and blended from outside the system, but they are obtained from an inactive dormant component silicate compound possessed by the material to be treated, and the dormant component silica, alumina component, calcium component and sodium oxide component The feature of the present invention is that it is activated and utilized. Therefore, the role of the modifying treatment agent that effectively and effectively exhibits the functionality capable of activating the dormant component at least at room temperature and enables detoxification treatment and shaping treatment is important.

上述してきたように本発明技術における改質処理剤は、改質対象素材の休眠成分を活性化するには強力なアルカリ性成分を必要とする。しかし、改質対象素材に共存する有害元素群を固定・不溶化するためには、有害元素群を容易に溶解せしめる過剰のアルカリ性成分はついで期待する水不溶性鉱物中にこれらの有害元素群を固定化するには不必要であり、ここに配合されるアルカリ性成分は必要であるが可能な限り必要最低限の量でよく、両者は拮抗状態の関係にある。したがって本発明の改質処理剤の構成内容と量割合は充分に管理されていることが大切である。  As described above, the modifying agent in the present technology requires a strong alkaline component to activate the dormant component of the material to be modified. However, in order to fix and insolubilize harmful element groups that coexist in the material to be modified, excess alkaline components that easily dissolve the harmful element groups are then immobilized in the expected water-insoluble minerals. It is not necessary to prepare the alkaline component, and the alkaline component contained therein is necessary but may be the minimum necessary amount, and both are in an antagonistic relationship. Therefore, it is important that the contents and amount ratio of the modifying treatment agent of the present invention are sufficiently controlled.

即ち、休眠成分を活性化するに必要な遊離のイオン性ナトリウムが充分に確保されてpH値12を超える状態にあることがまず必要である。しかし一方、改質対象素材に共存しているオキソ酸を形成する有害金属群(鉛、クロム、セレン)ならびに酸類元素群(ホウ素、フッ素)は、アルカリ成分と接すると容易に溶解する傾向にあり、オキソ酸を形成する有害金属群や酸類元素群を固定化するには系内にナトリウム成分が多く存在すると有害元素群の固定化を阻害する傾向にあり、充分に注意する必要がある。  That is, it is first necessary that the free ionic sodium necessary for activating the dormant component is sufficiently secured and the pH value exceeds 12. On the other hand, harmful metals (lead, chromium, selenium) and acid elements (boron, fluorine) that form oxoacids coexisting with the material to be modified tend to dissolve easily when in contact with alkali components. In order to immobilize the harmful metal group or acid element group that forms oxo acid, if there is a large amount of sodium component in the system, the immobilization of the harmful element group tends to be inhibited, and sufficient care must be taken.

特に本発明においては、少なくとも常温において、改質対象素材とする熱履歴ケートを構成する休眠成分が保有する成分類を有効に活用して、本発明の目的を達成させるには、ナトリウムイオンが大切な役割を果たすところに重要なポイントがある。したがって本発明においては、ナトリウムイオンが充分に活躍できる環境を整えて与えることが重要であり、本発明の改質処理剤を構成するときのナトリウムイオンは、多すぎても、また少なすぎても本発明の目的を期待通りに達成させることはできなお。  Particularly in the present invention, at least at room temperature, sodium ions are important in order to achieve the object of the present invention by effectively utilizing the components possessed by the dormant component constituting the heat history cake as the material to be modified. There is an important point where it plays a role. Therefore, in the present invention, it is important to prepare and provide an environment in which sodium ions can sufficiently play an active role, and even if there are too many or too few sodium ions when constituting the modifying treatment agent of the present invention. The object of the present invention cannot be achieved as expected.

本発明の改質処理剤は、改質処理機能を発揮する有効成分がカルシヤ、酸化ナトリウムならびに硫黄のオキシ酸の3成分で構成されていることを基本的としている。したがて、乾燥物における有効成分換算で表してカルシヤ含有成分に含まれるカルシヤ100質量部に対して、ナトリウム含有成分に含まれる酸化ナトリウムを0.1ないしは5質量部ならびに硫黄含有成分に含まれる硫黄を酸化物換算で1ないしは50質量部の酸化物基準で表した配合割合で3者成分がワンパック粉粒体を構成しており、該ワンパック粉粒体の水サスペンジョンpHが12を超えるアルカリ性であることが好ましい。  The modification treatment agent of the present invention is basically based on the fact that the effective component that exhibits the modification treatment function is composed of three components of calcium, sodium oxide, and sulfur oxyacid. Therefore, the sodium oxide contained in the sodium-containing component is contained in 0.1 to 5 parts by mass and the sulfur-containing component with respect to 100 parts by mass of the calcium contained in the calcium-containing component expressed in terms of the active ingredient in the dried product. The three-component component constitutes a one-pack granule with a blending ratio of 1 to 50 parts by mass of oxide in terms of oxide, and the water suspension pH of the one-pack granule exceeds 12. It is preferable that it is alkaline.

即ち、本発明においては、改質処理剤が改質処理機能を発揮する有効成分であるカルシヤ、酸化ナトリウムならびに硫黄のオキシ酸の3成分のみで構成される場合もあるが、有効成分を含有する化合物ないし組成物、特に改質対象素材となる熱履歴シリケート類、例えば廃棄物類がこれらの有効成分を含有する時は、これら有効成分を有効に活用することから、これらの熱履歴シリケート類を改質処理剤の配合原料に選部場合もある。  That is, in the present invention, the modifying treatment agent may be composed of only three components of calcium oxide, sodium oxide and sulfur oxyacid which are effective components that exhibit the modifying treatment function, but contains the effective components. When a compound or composition, especially heat history silicates that are materials to be modified, such as wastes, contain these active ingredients, these active ingredients are effectively used. In some cases, the modified raw material is selected as a blended raw material.

有効成分換算
したがって、本発明においては、本発明の改質処理剤の配合内容を表すに当たり、改質処理剤の構成を有効成分のみの改質処理剤の有効成分量で表す場合と、改質処理剤を構成せしめた有効成分を包含する原料の全体量からなる有姿量で表す場合の2通りを採用している。例えば(後述する参考例1の表7を参照)、有効成分であるカルシヤを46.7質量%含有する高炉スラグ100質量部ならびに有効成分である酸化ナトリウムを2.54質量%含有するボーキ赤泥100質量部で有姿の改質処理剤を構成せしめる時は、有姿量では100+100=200質量部の改質処理剤となるが、有効成分の換算量では46.7+2.54=49.24質量部となる。本明細書では改質処理剤原料の量を示す時、請求項ではこの有効成分換算量の数値をもって統一して表した。しかし一方、実施例では実配合を明らかにするため有姿量の数値をもって表し、改質処理剤原料が含有する有効成分含有量は別途示し、有効成分量での配合量換算を可能にした。
Therefore, in the present invention, in expressing the blending content of the modifying treatment agent of the present invention, the composition of the modifying treatment agent is expressed in terms of the effective component amount of the modifying treatment agent containing only the effective component, Two cases are used in the case where the treatment agent is expressed in a solid amount composed of the total amount of raw materials including the active ingredient constituting the treatment agent. For example (see Table 7 of Reference Example 1 described later), for example, 100 parts by mass of blast furnace slag containing 46.7% by mass of calcium as an active ingredient and baux red mud containing 2.54% by mass of sodium oxide as an active ingredient When 100 parts by mass of the solid modification treatment agent is configured, the quantity of solid treatment is 100 + 100 = 200 parts by mass of the modification treatment agent, but the converted amount of the active ingredient is 46.7 + 2.54 = 49.24. It becomes a mass part. In the present specification, when the amount of the raw material for the modification treatment agent is indicated, the claim is unified with the numerical value of the effective component conversion amount. On the other hand, in the examples, in order to clarify the actual composition, it was expressed by a numerical value of the solid amount, the active ingredient content contained in the reforming agent raw material was shown separately, and the compounding quantity conversion with the effective ingredient quantity was made possible.

本発明の改質処理剤において、カルシヤ含有成分に含まれる有効成分であるカルシヤ100質量部に対してナトリウム含有成分に含まれる有効成分である酸化ナトリウムが0.1質量部より少ないときは、改質処理剤におけるナトリウムイオンの活性化力が不足す傾向にあり好ましくない。したがって、改質処理剤における酸化ナトリウム成分の配合量は、休眠成分を少なくとも常温で活性化を可能とするに充分な量の配合量が配合されていることが必要である。  In the modification treatment agent of the present invention, when the amount of sodium oxide, which is an active ingredient contained in the sodium-containing component, is less than 0.1 part by mass with respect to 100 parts by mass of the active ingredient contained in the calcium-containing component, It is not preferable because the activation power of sodium ions in the quality treatment agent tends to be insufficient. Therefore, the blending amount of the sodium oxide component in the modifying treatment agent needs to be blended in a sufficient amount so that the dormant component can be activated at least at room temperature.

一方、有効成分である酸化ナトリウム成分が5質量部より多く配合する時は、系内で改質対象素材と改質処理剤で水を介して形成する活性化混和物内におけるナトリウムイオンの活性化力が多すぎて、次いで形成する水不溶性鉱物の形成において、アルカリ性成分に溶解性の高いオキソ酸元素群である鉛、クロム、ヒ素、セレンおよびホウ素からなるグループ、さらにハロゲン酸である酸類元素であるフッ素はナトリウムイオンで容易に溶解し、形成する水不溶性鉱物に固定化すること難しい傾向にあり好ましくない。  On the other hand, when more than 5 parts by mass of the sodium oxide component, which is an active ingredient, is added, activation of sodium ions in the activated admixture formed through the water with the material to be modified and the modifying treatment agent in the system In the formation of water-insoluble minerals that are too powerful and then formed, the group consisting of lead, chromium, arsenic, selenium and boron, which are highly soluble in alkaline components, and also acid elements that are halogen acids Certain fluorine is not preferable because it easily dissolves with sodium ions and tends to be difficult to fix to the water-insoluble mineral formed.

本発明の改質処理剤において、カルシヤ含有成分に含まれる有効成分であるカルシヤ100質量部に対して硫黄含有成分に含まれる有効成分である硫黄を酸化物換算で1質量部より少ないときは、共配合されているカルシウムイオンを次なるステップで中和し、またマトリック形成に必要な水和鉱物の形成が不足して、形成マトリックに所定の強度を期待することができない。また一方硫黄酸化物成分が50質量部より多いときは、改質処理剤の水サスペンジョンpH値を12以上に確保することが困難となる傾向にあり、しかも改質対象素材の休眠成分を活性化するに必要なナトリウムイオンならびにカルシウムイオンを早々に中和して不活性化させてしい好ましくない。  In the modification treatment agent of the present invention, when sulfur, which is an active ingredient contained in a sulfur-containing component, is less than 1 part by mass in terms of oxide with respect to 100 parts by mass of calcia, which is an active ingredient contained in a calcium-containing component, The co-mixed calcium ions are neutralized in the next step, and the formation of hydrated minerals necessary for matrix formation is insufficient, and the formation matrix cannot be expected to have a predetermined strength. On the other hand, when the sulfur oxide component is more than 50 parts by mass, it tends to be difficult to ensure the water suspension pH value of the modifying agent to 12 or more, and the dormant component of the material to be modified is activated. Therefore, it is not preferable that sodium ions and calcium ions necessary for the treatment are quickly neutralized and inactivated.

カルシヤ含有成分
本発明改質処理剤を構成するカルシヤ含有成分は、一般に試薬、工業薬品、試作品、工業薬品、工業用資材、廃棄物類等から、酸化物基準で表して有効成分であるカルシヤを少なくとも25質量%含有している粉粒体のカルシヤ含有の化合物ないしは組成物の中から好適に選び挙げることができる。
Calcium-containing components Calcium-containing components that constitute the modification treatment agent of the present invention are generally active ingredients expressed on the oxide basis from reagents, industrial chemicals, prototypes, industrial chemicals, industrial materials, wastes, etc. Can be suitably selected from among a calcium-containing compound or composition in a granular form containing at least 25% by mass.

本発明改質処理材を構成するカルシヤ含有成分の代表的な例としては、天然・合成、副生されるカルシヤを主成分とする酸化カルシウム(生石灰)または水酸化カルシウム(消石灰)を好適に挙げることができる。酸化カルシウムは、石灰岩等の炭酸カルシウムを約950℃以上で脱炭酸して生石灰として大量に生産されており、鉄鋼、化学工業、紙、建材、肥料、農薬、土壌改良等の広い分野で使用されて安価に入手することから好ましい。しかし、カルシヤ(生石灰:酸化カルシウム)は、水と接すると水と激しく反応して多量の熱量(1モルで15540cal.)を発生し、また空気大気中の水や炭酸と容易に反応して炭酸塩や水酸化物に変質して改質処理剤の貯蔵安定性を損なうことから、改質処理剤の配合には充分注意する必要がある。  As a typical example of the calcium-containing component constituting the modified material of the present invention, calcium oxide (quick lime) or calcium hydroxide (slaked lime) mainly composed of natural, synthetic, and by-produced calcium oxide is preferably exemplified. be able to. Calcium oxide is produced in large quantities as quick lime by decarboxylating calcium carbonate such as limestone at about 950 ° C or higher, and is used in a wide range of fields such as steel, chemical industry, paper, building materials, fertilizer, agricultural chemicals, and soil improvement. It is preferable because it is inexpensive and available. However, calcium oxide (quick lime: calcium oxide) reacts violently with water to generate a large amount of heat (15540 cal. Per mole), and easily reacts with water and carbonic acid in the air atmosphere to produce carbonic acid. It is necessary to pay close attention to the blending of the modification treatment agent because it changes into a salt or a hydroxide and impairs the storage stability of the modification treatment agent.

またカルシヤ成分には、カルシウム元素と同族元素のアルカリ土類金属のマグネシウム、亜鉛、ストロンチウムならびにバリリウム元素等が混在共存する場合があり、10質量%以下の量で混在する限り、本発明の基本的作用機能等を損なうものではなく構わない。カルシウム成分の他の具体的例としては、天然鉱物、もしくは工業薬品、さらには副生される廃棄物類の中から、塩基性ないし正塩化合物であるアルミン酸カルシウム、ケイ酸カルシウム、炭酸水素カルシウム、炭酸ケイ素カルシウム、塩基性の硫酸カルシウム、硝酸カルシウム、リン酸カルシウム、リン鉱石、石灰石、塩化カルシウム、ケイ酸カルシウム鉱物等であり、カルシウムイオンとしての活性化を発揮できる化合物や組成物群から適宜選ぶことができる。  In addition, the calcium component may coexist with the alkaline earth metals magnesium, zinc, strontium, and barium elements, which are the elements of the calcium and the same family, and the basic component of the present invention as long as it is mixed in an amount of 10% by mass or less. The function and the like are not impaired. Other specific examples of the calcium component include natural minerals, industrial chemicals, and by-products such as calcium aluminate, calcium silicate, and hydrogen carbonate, which are basic or normal salt compounds. , Calcium carbonate, basic calcium sulfate, calcium nitrate, calcium phosphate, phosphate ore, limestone, calcium chloride, calcium silicate mineral, etc., selected from compounds and compositions that can activate as calcium ions, as appropriate Can do.

また、熱履歴シリケートの中から有効成分であるカルシウム成分を充分に含有する休眠成分である含カルシウム休眠成分を選ぶこともできる。これらの具体的な含カルシウム休眠成分としては、ゴミ類の焼却処理時に排気ガス等の処理に採択した石灰を包含している焼却灰類、製鉄業界で製鉄生産時に石灰塩で排出される高炉・製鋼スラグ類、保温剤ないしは断熱材等に使用されて廃棄されたケイ酸カルシウム類の廃材、カルシウム塩鉱物を主成分とするセメント類、石膏ボードや化学工場や排煙処理等からの副生する石こう、ならびに各種のケイ酸塩化合物の群より選ばれる単独ないし2種以上の組み合わせの休眠成分からなる熱履歴シリケートを好適に挙げることができる。  In addition, a calcium-containing dormant component that is a dormant component that sufficiently contains a calcium component that is an active ingredient can be selected from heat history silicates. These specific calcium-containing dormant components include incineration ash that includes lime adopted for the treatment of exhaust gas, etc. during the incineration of garbage, blast furnaces that are discharged as lime salt during iron production in the steel industry Used as steelmaking slag, waste materials of calcium silicates used for heat insulation or insulation, cements mainly composed of calcium salt minerals, gypsum boards, chemical factories, and by-product from smoke treatment Preferable examples include heat history silicates composed of gypsum and a dormant component of one or a combination of two or more selected from the group of various silicate compounds.

この有効成分であるカルシウム成分を含有する熱履歴シリケートを採択するときは、酸化物基準で表して有効成分のカルシウム成分を少なくとも20質量%の量で確保している含カルシウム休眠成分100質量部に対して、遊離のイオン性ナトリウムを有する例えば活性な水酸化ナトリウムとの組み合わせで構成されるナトリウム成分を3質量部以下の量で添加配合されている粉粒体が好ましい。さらに含カルシウム休眠成分にナトリウム成分が添加配合されている粉粒体に水を450質量部以下の量で加え複合されて遊離のイオン性ナトリウムが確保されており、水サスペンジョンpH値が12を超える固形体または液状体である含カルシウム休眠成分を好適に挙げることができる。  When adopting a heat history silicate containing a calcium component which is an active ingredient, 100 parts by mass of a calcium-containing dormant ingredient which is ensured in an amount of at least 20% by mass of the calcium ingredient of the active ingredient expressed on an oxide basis. On the other hand, a granular material in which a sodium component composed of a combination with, for example, active sodium hydroxide having free ionic sodium is added and blended in an amount of 3 parts by mass or less is preferable. Further, water is added to the granular material in which the sodium component is added to the calcium-containing dormant component and added in an amount of 450 parts by mass or less to ensure free ionic sodium, and the water suspension pH value exceeds 12. A calcium-containing dormant component that is a solid or liquid can be preferably exemplified.

ナトリウム含有成分
本発明の改質処理剤を構成するナトリウム含有成分は、一般に試薬、工業薬品、試作品、工業薬品、工業用資材、廃棄物類等から、酸化物基準で表して有効成分である酸化ナトリウムを少なくとも2質量%含有している粉粒体のナトリウム含有の化合物ないしは組成物の中から好適に選び挙げることができる。
Sodium-containing component The sodium-containing component constituting the modifying agent of the present invention is generally an active ingredient expressed on the oxide basis from reagents, industrial chemicals, prototypes, industrial chemicals, industrial materials, wastes, etc. A powdery sodium-containing compound or composition containing at least 2% by mass of sodium oxide can be preferably selected.

これらのナトリウム含有成分としては、工業薬品として広く生産されており入手も容易である水酸化ナトリウム(苛性ソーダ)を好適に挙げることができる。ナトリウム含有成分の他の具体的例としては、硫酸ナトリウム、塩化ナトリウム、炭酸ナトリウム、重炭酸ナトリウム、硝酸ナトリウム、アルミン酸ナトリウム、ホウ酸ナトリウム、リン酸ナトリウム、ケイ酸ナトリムならびに酸化性ナトリウム塩化合物の群より選ばれる単独ないし2種以上の組み合わせナトリウム塩化合物の正塩または塩基性塩からなる粉粒体を好適に挙げることができる。  Preferred examples of these sodium-containing components include sodium hydroxide (caustic soda) that is widely produced as an industrial chemical and is easily available. Other specific examples of sodium-containing ingredients include sodium sulfate, sodium chloride, sodium carbonate, sodium bicarbonate, sodium nitrate, sodium aluminate, sodium borate, sodium phosphate, sodium silicate and oxidizable sodium salt compounds. Preferable examples include powders composed of a normal salt or a basic salt of a single or two or more combined sodium salt compounds selected from the group.

特にナトリウム含有成分として、硫酸塩である硫酸ナトリウム(芒硝)を選ぶ時は、本発明改質処理剤を構成するナトリウム含有成分と硫黄含有成分の役割を一つの化合物で2役を果たすことができることから大変好ましい。硫酸ナトリウムの場合、併配合するカルシヤ含有成分のカルシウムイオンと予め硫酸根が反応して、カルシウムイオンの中で遊離のナトリウムイオンを形成できることからも好ましい。  In particular, when sodium sulfate (sodium salt), which is a sulfate, is selected as the sodium-containing component, the role of the sodium-containing component and the sulfur-containing component constituting the modification treatment agent of the present invention can be played by two compounds. Is very preferable. In the case of sodium sulfate, calcium ions of the calcium-containing component to be blended together with sulfate radicals react in advance to form free sodium ions in the calcium ions.

さらにナトリウム含有成分の代表的な他の具体例としては、ハロゲン化合物である塩化ナトリウム(食塩)を挙げることができる。勿論、本発明改質処理剤中にハロゲンである塩素が混入されても本発明の作用機構を本質的に阻害するものではない。しかし、形成される結着形状体が鉄等の金属と接触するケースでは好ましくない場合がある。また、本発明ナトリウム含有成分には、ナトリウム元素と同属元素であるカリまたはリチウムが共存する場合がある。カリならびにリチウムがナトリウム塩化合物に共存することは基本的に本発明処理材の処理機能を阻害するものではない。  Furthermore, another specific example of the sodium-containing component is sodium chloride (salt) which is a halogen compound. Of course, even if chlorine, which is a halogen, is mixed in the modifying treatment agent of the present invention, the action mechanism of the present invention is not essentially inhibited. However, it may not be preferable in the case where the formed binding body is in contact with a metal such as iron. The sodium-containing component of the present invention may coexist with potassium or lithium, which is the same element as the sodium element. The coexistence of potassium and lithium in the sodium salt compound basically does not hinder the treatment function of the treatment material of the present invention.

また、本発明改質処理剤においては、ナトリウム含有成分が予め水系溶媒に溶解・混和している含水体として、下記組成式(1)

Figure 2006247645
[式中:Mはナトリウムないしカリウム元素、aは0.1ないし4の数、wは16ないし50の数]で表されるケイ酸アルカリの群より選ばれる単独ないし2種以上の組み合わせの粉状体もあるが、液状の含水体のケイ酸アルカリを挙げることもできる。Further, in the modified treatment agent of the present invention, as a hydrous material in which a sodium-containing component is previously dissolved and mixed in an aqueous solvent, the following composition formula (1)
Figure 2006247645
[Wherein, M is an element of sodium or potassium, a is a number of 0.1 to 4, w is a number of 16 to 50] single or a combination of two or more selected from the group of alkali silicates Although there is a state body, the liquid hydrated body alkali silicate can also be mentioned.

アルカリケイ酸塩のアルカリ金属は、一般に入手容易であり、安価であるナトリウムが好適である。本発明改質処理剤における硫黄含有成分としてのアルカリ補充組成物ならびにケイ酸塩補充組成物としてケイ酸とナトリウムを同時に補給できることから好ましい。アルカリケイ酸塩のナトリウム塩は、水ガラスとしてJIS化されており、工業的にも大量生産されており、また粉状体あり好適である。しかし、アルカリケイ酸塩は一般的に液状態で製品化されているが、液状態のアルカリケイ酸塩では、液体の担持・吸着能力を有する本発明の混合原料類に担持・吸着させて採択することができる。  The alkali metal of the alkali silicate is generally easily available and inexpensive sodium is preferable. The alkali replenishing composition as the sulfur-containing component and the silicate replenishing composition in the present modification treatment agent are preferable because silicic acid and sodium can be replenished simultaneously. The sodium salt of alkali silicate has been JIS-converted as water glass, is industrially mass-produced, and is preferably in the form of powder. However, alkali silicates are generally commercialized in the liquid state, but liquid alkali silicates are adopted by being supported and adsorbed on the mixed raw materials of the present invention having the ability to support and adsorb liquids. can do.

さらにまた、本発明の改質処理剤を構成するナトリウム含有成分として、改質対象素材である熱履歴シリケートの中から有効成分である酸化ナトリウム成分を含有している休眠成分である含ナトリウム休眠成分を選ぶこともできる。含ナトリウム休眠成としては、ゴミ焼却灰、汚泥焼却灰、ボーキサイトからアルミナを回収した残渣である赤泥ないし芒硝類廃液の回収物の群より選ばれる単独ないし2種以上の組み合わせの休眠成分からなる熱履歴シリケートに共存して有効成分である酸化ナトリウム成分を酸化物基準で表して少なくとも1.5質量%含有する含ナトリウム休眠成分であり、このとき改質処理剤を構成するカルシヤ含有成分が、活性な酸化カルシウムないし水酸化カルシウムである粉粒体ないし含水体で構成される改質処理剤を好適に選ぶことができる。  Furthermore, as a sodium-containing component constituting the modifying treatment agent of the present invention, a sodium-containing dormant component that is a dormant component that contains a sodium oxide component that is an active component from a heat history silicate that is a material to be modified You can also choose. The sodium-containing dormancy is composed of single or a combination of two or more kinds of dormant components selected from the group of waste incineration ash, sludge incineration ash, red mud that is a residue of alumina recovered from bauxite, or a collection of waste liquids of mirabilite. It is a sodium-containing dormant component containing at least 1.5% by mass of the sodium oxide component which is an active ingredient coexisting with the heat history silicate, and at this time, the calcium-containing component constituting the modifying treatment agent, A modification treatment agent composed of a granular material or a hydrated body which is active calcium oxide or calcium hydroxide can be suitably selected.

硫黄含有成分
本発明の改質処理剤を構成する硫黄含有成分が、一般に試薬、工業薬品、試作品、工業薬品、工業用資材、廃棄物類等から、無水物の硫黄酸化物基準で表して有効成分を少なくとも18質量%含有している硫黄のオキシ酸化合物ないし硫化物からなる粉粒体の硫黄含有成分の化合物ないしは組成物の中から好適に選び挙げることができる。
Sulfur-containing components Sulfur-containing components constituting the modifying treatment agent of the present invention are generally expressed on the basis of anhydrous sulfur oxides from reagents, industrial chemicals, prototypes, industrial chemicals, industrial materials, wastes, etc. A sulfur-containing component compound or composition of a granular material comprising a sulfur oxyacid compound or sulfide containing at least 18% by mass of an active ingredient can be preferably selected.

特に、本発明における硫黄含有成分は、形成される結着形状体のpH値10未満を確保する役割を担える改質処理剤であることが好ましい。また、本発明改質処理材により形成される複合母体を構成する水和型の硫酸カルシウムを主体とするケイ酸カルシウム、アルミノケイ酸カルシウム等は結着形状体に緻密性を付与して強度を効果的に補強することから大変好ましい。  In particular, the sulfur-containing component in the present invention is preferably a modification treatment agent capable of ensuring a pH value of less than 10 of the formed binder. In addition, calcium silicate, calcium aluminosilicate, etc., mainly composed of hydrated calcium sulfate, which constitutes the composite matrix formed by the modified treatment material of the present invention, gives strength to the bound shape body by providing denseness. It is very preferable because it is reinforced.

本発明の硫黄含有成分に一般的な化合物は、一般的に下記組成式(4)

Figure 2006247645
[式中:Mはアルカリ金属、Zはアルカリ土類金属、Rはアルミニウムまたは3価の鉄、a、b、cは零を含む20以下の数、nは2または3の数、wは零を含む25以下の数]で表される金蔵元素の硫黄のオキシ酸塩化合物の塩基性塩または正塩の群より選ばれる単独ないし2種以上の組み合わせの硫酸根保有化合物もしくは硫酸根保有組成物で構成されている粉粒体を好適に挙げることができる。The general compound for the sulfur-containing component of the present invention generally has the following composition formula (4):
Figure 2006247645
[Wherein, M is an alkali metal, Z is an alkaline earth metal, R is aluminum or trivalent iron, a, b and c are numbers of 20 or less including zero, n is a number of 2 or 3, and w is zero. A sulphate-bearing compound or a sulphate-bearing composition of a single or a combination of two or more selected from the group consisting of a basic salt or a normal salt of a sulfur oxyacid salt compound of a metallographic element represented by The granular material comprised by can be mentioned suitably.

特に、本発明改質処理剤を構成する硫黄含有成分としては、アルカリ金属、アルミニウムないしは鉄のオキシ酸の硫酸塩を主成分とする硫酸根・亜硫酸含有の化合物または組成物もしくはアルカリ金属、アルミニウムないしは鉄の硫化物を主成分とする硫化物含有組成物の単独ないし2種以上の組み合わせで構成される粉粒体であり、併配合するカルシヤ含有成分と中和反応する機能を有す硫黄含有成分であることが好ましい。  In particular, the sulfur-containing component constituting the modifying treatment agent of the present invention includes an alkali metal, aluminum or iron sulfate oxyacid sulfate-containing compound or composition containing as a main component or an alkali metal, aluminum or Sulfur-containing component that is composed of a single or a combination of two or more sulfide-containing compositions containing iron sulfide as a main component and has a function of neutralizing reaction with a calcium-containing component that is mixed together It is preferable that

本発明で採択できる硫黄含有成分は、硫酸・亜硫酸根、もしくは硫化物を含む化合物または組成物であれば構わないが、汎用されるアルカリ金属の硫黄のオキシ酸塩を主成分とする芒硝型組成物、もしくは硫酸アルミニウムを主成分とする明礬型組成物の2種類を好適な硫黄含有成分として挙げることができる。  The sulfur-containing component that can be adopted in the present invention may be any compound or composition containing sulfuric acid, sulfite group, or sulfide. Or two types of clear compositions containing aluminum sulfate as a main component can be cited as suitable sulfur-containing components.

本発明の硫黄含有成分における明礬組成物としては、下記組成式(5)

Figure 2006247645
[式中:Mはアルカリ金属、Rは3価のアルミニウムないし鉄、aは0.2ないし20の数、cは1ないし20の数、wは零を含む25以下の数、nは2または3の数]で表されるアルカリ金属を含むアルミニウムまたは鉄の硫黄のオキシ酸塩の各塩類群より選ばれる単独ないし2種以上組み合わせの明礬型組成物、また明礬型組成物であるアルカリ金属のアルミニウムまたは鉄の硫黄のオキシ酸塩としては、硫酸アルミニウムと硫酸カリウムとの混合溶液から生成する正八面体の複塩結晶が代表的である。As a clear composition in the sulfur-containing component of the present invention, the following composition formula (5)
Figure 2006247645
[Wherein, M is an alkali metal, R is trivalent aluminum or iron, a is a number of 0.2 to 20, c is a number of 1 to 20, w is a number of 25 or less including zero, n is 2 or Or a combination of two or more selected from a salt group of an aluminum or iron sulfur oxyacid salt containing an alkali metal represented by the number of 3], or an alkali metal that is an alum-type composition A typical example of the aluminum or iron sulfur oxyacid salt is an octahedral double salt crystal formed from a mixed solution of aluminum sulfate and potassium sulfate.

しかも本発明改質処理剤による固化・硬化製品にはゼオライト類の生成を期待することから、ゼオライト類の構成成分であるアルミニウム成分を同時に共存せしめられることは好ましい。したがって、硫酸根成分と共にアルミニウム成分が共存している明礬型組成物は有効である。また、重金属類の固定化対象としてひ素が共存するときは、鉄イオンが配合されているときは、鉄イオンがひ素の固定化に有効であり、鉄含有の明礬型組成物は有効であり効果的である。したがって、工業薬品の水改質処理剤等として汎用されている粉状体の硫酸アルミニウム(バンド)は、本発明の硫黄含有成分原料として好適であり、さらに粘土等の鉱物を硫酸処理したときに廃酸として副生される鉄を含んだ含鉄硫酸アルミニウムは、好適に採択することができる。  In addition, since the formation of zeolites is expected in the solidified / cured product obtained by the present modification treatment agent, it is preferable that the aluminum component which is a constituent component of the zeolites coexist at the same time. Therefore, a clear composition in which an aluminum component coexists with a sulfate radical component is effective. In addition, when arsenic coexists as an immobilization target for heavy metals, when iron ions are added, iron ions are effective for immobilizing arsenic, and iron-containing alum-type compositions are effective and effective. Is. Therefore, the powdered aluminum sulfate (band), which is widely used as a water-modifying treatment agent for industrial chemicals, is suitable as the sulfur-containing component raw material of the present invention, and further when a mineral such as clay is subjected to sulfuric acid treatment. An iron-containing aluminum sulfate containing iron by-produced as a waste acid can be preferably adopted.

本発明の硫黄含有成分における芒硝型組成物としては、アルカリソルトでもある下記組成式(6)

Figure 2006247645
[式中:Mはアルカリ金属元素、aは1ないし20の数、wは零を含む20以下の数、nは2または3の数]で表される塩基性塩もしくは正塩のリチウム、ナトリウムもしくはカリウムであるアルカリ金属の硫黄のオキシ酸塩化合物の群より選ばれる単独ないし2種以上の組み合わせの芒硝型組成物を好適に挙げることができる。As the salt-type composition in the sulfur-containing component of the present invention, the following composition formula (6), which is also an alkali salt:
Figure 2006247645
[Wherein, M is an alkali metal element, a is a number of 1 to 20, w is a number of 20 or less including zero, and n is a number of 2 or 3] Alternatively, a single salt type or a combination of two or more types selected from the group of alkali metal sulfur oxyacid salt compounds which are potassium can be preferably mentioned.

本発明硫黄含有成分における芒硝型組成物であるリチウム、ナトリウムもしくはカリウムであるアルカリ金属の硫黄のオキシ酸塩化合物における代表的な化合物は、天然産または合成・副生の有水もしくは無水の芒硝(硫酸ナトリウム)、天然の岩塩産地で産する石灰芒硝である複塩等を挙げることができる。また、工業的には、人絹や廃液等の廃液処理時の副生芒硝等として副生されている。不純物を含む天然または合成・副生の芒硝も好適に採択することができる。  The representative compound in the oxyacid salt compound of alkali metal sulfur which is lithium, sodium or potassium, which is the mirabilite type composition in the sulfur-containing component of the present invention, is a natural or synthetic or by-product hydrated or anhydrous mirabilite ( Sodium sulfate) and double salt which is lime salt salt produced in natural rock salt production areas. Moreover, industrially, it is by-produced as by-product mirabilite etc. at the time of waste liquid processing, such as human silk and waste liquid. Natural or synthetic or by-product mirabilite containing impurities can also be suitably adopted.

またカリウムを含む複塩や塩基性塩、アルカリ土類金属の塩化合物、炭酸塩を共存している混合塩等を含む化合物も、芒硝型組成物として好適に採択することができる。勿論ここで採択できる芒硝型組成物である硫酸ナトリウムは、水溶出pH値を13未満の範囲で確保して、活性化活用成分を構成するナトリウム含有成分とし重要な構成成分であり、ナトリウム成分として配合されると共に同時に硫黄含有成分として配合され、2者の機能性を同一化合物で同時に果たせることから効率もよく好ましい。  In addition, a compound containing a double salt or basic salt containing potassium, a salt compound of an alkaline earth metal, a mixed salt coexisting with a carbonate, or the like can also be suitably adopted as the mirabilite type composition. Of course, sodium sulfate, which is a salt-type composition that can be adopted here, is an important component as a sodium-containing component that constitutes an activation utilization component by securing a water elution pH value in the range of less than 13, Since it is mix | blended and it mix | blends simultaneously as a sulfur-containing component and can fulfill | perform two functions simultaneously with the same compound, it is also efficient and preferable.

本発明の硫黄含有成分として選ばれる硫化物含有組成物としては、硫化ナトリウム、硫化カルシウム、硫化マグネシウム、硫化アルミニウム、硫化鉄ないしは硫化鉱物の群より選ばれる単独ないし2種以上の組み合わせの粉粒体を好適にあげることができる。この中で硫化ナトリウムは、ナトリウムを含んでいることから、ナトリウム含有成分とすることもできるが、硫化ナトリウムは、空気中で容易に分解して硫酸ナトリウムに変化することから、特に改質処理剤の水溶出pHへの影響に注意して扱う必要がある。  The sulfide-containing composition selected as the sulfur-containing component of the present invention includes a single or a combination of two or more powders selected from the group of sodium sulfide, calcium sulfide, magnesium sulfide, aluminum sulfide, iron sulfide or sulfide mineral Can be preferably mentioned. Among them, sodium sulfide contains sodium and can be used as a sodium-containing component. However, sodium sulfide is easily decomposed in air and converted into sodium sulfate. It is necessary to handle with care to the effect of water on the water elution pH.

硫化物含有組成物としては、天然硫塩鉱物を含む硫化鉱物である黄鉄鉱、車骨鉱、鶏冠石等を選びことができる。しかし、これら硫化鉱物には硫黄に類似したセレン,テルル,砒素,アンチモン,蒼鉛の金属元素、ならびに銀・水銀・銅・鉛・亜鉛・モリブデンの金属元素を共存している場合が多いことから、充分注意して取り扱う必要がある。  As the sulfide-containing composition, pyrite, car bone ore, poultry stone, and the like, which are sulfide minerals including natural sulfate minerals, can be selected. However, these sulfide minerals often contain selenium, tellurium, arsenic, antimony, and lead metal elements similar to sulfur, and silver, mercury, copper, lead, zinc, and molybdenum metal elements. It must be handled with great care.

以上示してきた本発明における改質処理剤を構成する硫黄含有成分になる硫酸根保有組成物や硫化物含有組成物は、一般に工業薬品としても入手は容易であるが、産業界における化学工業界、電力業界、排煙処理業界等から廃棄物や副生物として排出されており、安価な廃棄物類のリサイクル品としての活用・利用が有効であり、硫酸根保有組成物や硫化物含有組成物の供給の場は広く、これらの硫酸根保有組成物ならびに硫化物含有組成物類を活用・利用することは、廃棄物のリサイクル利用の立場から好ましい。  The sulfate group-containing composition and the sulfide-containing composition, which are the sulfur-containing components constituting the modifying treatment agent of the present invention described above, are generally easily available as industrial chemicals. It is discharged from the electric power industry, smoke treatment industry, etc. as waste and by-products, and it can be effectively used and used as a recycled product of inexpensive waste. Is widely used, and utilization and utilization of these sulfate radical-containing compositions and sulfide-containing compositions is preferable from the viewpoint of recycling waste.

[改質処理方法]
本発明技術における改質処理方法は、大きく2通りの活用方法に分類することができる。その一つは、本発明で処理対象素材とする熱履歴シリケートに本発明改質処理剤を混和・活性化して調製される活性化混和物自身を結着・硬化せしめて各種の自己完結型の結着形状体に改質処理する自己完結型活用方法である。もう一つは、本発明で処理対象素材とする熱履歴シリケートに本発明改質処理剤を混和・活性化して予め調製される活性化混和物を付着剤として、別途選ばれた応用対象基材表面に固結、結着、付着、被覆等の付着手段により付着せしめて各種の基材付着型の結着形状体に改質処理する基材付着型活用方法である。
[Modification method]
The reforming treatment method in the technology of the present invention can be roughly classified into two utilization methods. One of them is that various kinds of self-contained types are prepared by binding and curing the activated admixture itself prepared by mixing and activating the modified treatment agent of the present invention to the heat history silicate as the material to be treated in the present invention. This is a self-contained utilization method that modifies the bound shape. The other is a base material for application selected separately, using an activated admixture prepared in advance by admixing and activating the modified treatment agent of the present invention in the heat history silicate as the material to be treated in the present invention. This is a substrate adhesion type utilization method in which the surface is adhered to the surface by adhesion means such as consolidation, binding, adhesion, coating, etc., and modified into various substrate adhesion type binding shapes.

本発明の自己完結型活用方法は、本発明の改質処理剤を活用して、必要に応じて機能付与剤を付加して少なくとも常温で水系溶媒を介して、改質対象素材となる休眠成分からなる熱履歴シリケートに加えて活性化混和物とする混和工程、必要に応じて該活性化混和物を形状化処理物とする加工工程、次いで該活性化混和物ないし該形状化処理物を所定雰囲気中に開放せしめて結着形状体とする養生工程で構成される一連の作業工程からなる改質処理方法で構成されている。  The self-contained utilization method of the present invention utilizes the modification treatment agent of the present invention, adds a function-imparting agent as necessary, and at least at room temperature via an aqueous solvent, a dormant component that becomes a material to be modified In addition to a heat history silicate comprising an activated admixture, a processing step in which the activated admixture is shaped into a processed product, if necessary, and then the activated admixture or the shaped processed product It is comprised by the modification | reformation processing method which consists of a series of work processes comprised by the curing process open | released in atmosphere and setting it as a binding shape body.

本発明の改質処理方法において好適に採択される機能付与剤は、サプリメント、インプルーブメント、ファンクションメントもしくはレインホースメントの単独ないし2種以上の組み合わせの粒径500μ以下の粉粒体で構成されていることが好ましい。勿論、本発明技術に採択される機能付与剤は、ここに示した機能付与剤に限定されるものではなく、上記した機能付与剤に類似した機能性付与を発揮できる化合物ないしは組成物類が選ばれることを拒むものではない。  The function-imparting agent suitably adopted in the modification treatment method of the present invention is composed of a powder, having a particle size of 500 μm or less, which is a supplement, improvement, functionment or rain reinforcement alone or in combination of two or more. Preferably it is. Of course, the function-imparting agent adopted in the technology of the present invention is not limited to the function-imparting agent shown here, and a compound or a composition that can provide functionalities similar to the function-imparting agent described above is selected. It does not refuse to be done.

本発明改質処理方法の一連の作業工程における混和工程は、処理対象素材である原位置または持込位置に存在する熱履歴シリケートを乾燥物基準で100質量部に対して、改質処理剤を乾燥物基準で2ないし20質量部未満を加え、必要に応じて機能付与剤を400質量部以下の量で付加して混和して活性化混和物とし、該活性化混和物中の含有水分の含水率が10ないし70質量%範囲に確保される状態になるように必要に応じて水系溶媒を加えて量割合を調整して混和し、該活性化混和物が常温にて混和・放置される3時間の間のpH値が12を超える状態が確保されてバサバサ状、可塑状、マヨネーズ状、糊状ないしはスラリー状の混和物に調製される工程である。  In the mixing step in the series of work steps of the present modification treatment method, the heat treatment silicate present at the original position or the carry-in position as the material to be treated is added to 100 parts by mass on the basis of dry matter, and the modification treatment agent is added. Add 2 to less than 20 parts by weight on a dry matter basis, add a function-imparting agent in an amount of 400 parts by weight or less as necessary, and mix to make an activated mixture, and the moisture content in the activated mixture A water-based solvent is added as necessary to adjust the proportion so that the water content is maintained in the range of 10 to 70% by mass, and the activated mixture is mixed and left at room temperature. This is a process in which a state in which the pH value for 3 hours exceeds 12 is secured, and the mixture is prepared into a mixture in the form of frustration, plastic, mayonnaise, paste or slurry.

次いで、本発明改質処理方法の一連の作業工程における加工工程は、必要に応じて上記の活性化混和物を原位置非成型物、耐水性粉粒体物ないしは形状加工成型物からなる形状化処理物に加工形状化処理する工程である。  Next, the processing step in a series of work steps of the modified treatment method of the present invention is performed by shaping the activated admixture from an in-situ non-molded product, a water-resistant granular material or a shape-processed molded product, if necessary. It is a process of processing and shaping the processed material.

さらに本発明改質処理方法の一連の作業工程における養生工程は、上記の混和工程で調製された活性化混和物、ないしは上記の加工工程で調製された形状化処理物を常温から100℃範囲にある常圧、加圧、減圧条件下における気中、水中、海中、土中、溶液中、蒸気中、非酸素ガス中の雰囲気の群より選ばれる単独雰囲気中ないし2種以上の組み合わせの多段雰囲気中に少なくとも15分間解放して反応・養生を進行せしめて結着硬化が完了している自己完結型の原位置非成型品、耐水性粉粒体品ないしは形状加工成型品からなる結着形状体とする工程である。  Further, the curing process in the series of work steps of the modification treatment method of the present invention is to bring the activated admixture prepared in the above mixing process or the shaped processed product prepared in the above processing process into a range from room temperature to 100 ° C. In a single atmosphere selected from the group of air, water, sea, soil, solution, steam, and non-oxygen gas atmosphere under a certain normal pressure, pressurization, and decompression conditions, or a multistage atmosphere of a combination of two or more. A self-contained in-situ non-molded product, a water-resistant granular product or a shape-processed molded product that has been released for at least 15 minutes, and has undergone a reaction / curing process to complete binding and curing. It is a process.

また一方、本発明の基材付着型の活用方法は、予め本発明の改質処理剤を活用して、必要に応じて機能付与剤を付加して少なくとも常温で水系溶媒を介して改質対象素材となる休眠成分からなる熱履歴シリケートに加える混和工程で調製される流動性活性化混和物を予め用意された応用対象基材に付着せしめる加工工程により付着化処理物として調製し、次いで該付着化処理物を所定雰囲気中に開放せしめて応用対象基材と一体化された結着形状体とする養生工程で構成される一連の作業工程からなる改質処理方法で構成されている。  On the other hand, the method for utilizing the substrate adhesion type of the present invention uses the modification treatment agent of the present invention in advance, adds a function-imparting agent as necessary, and is subject to modification via an aqueous solvent at least at room temperature. The fluidity activated admixture prepared in the admixing step added to the heat history silicate composed of the dormant component as the material is prepared as an adhering treatment product by the processing step of adhering to the application target substrate prepared in advance. It is comprised by the modification | reformation processing method which consists of a series of work processes comprised by the curing process which makes a chemical-treatment thing open | release in predetermined atmosphere, and makes it the binding shape body integrated with the application object base material.

本発明改質処理方法の一連の作業工程における混和工程において調製される流動性活性化混和物は、処理対象素材である原位置または持込位置に存在する熱履歴シリケートを乾燥物基準で100質量部に対して、改質処理剤を乾燥物基準で2ないし20質量部未満を加え、必要に応じて機能付与剤を400質量部以下の量で付加して混和して活性化混和物とし、該活性化混和物中の含有水分の含水率が35ないし70質量%範囲に確保される状態になるように水系溶媒を加えて量割合を調整して混和し、該活性化混和物が常温にて混和・放置される3時間の間のpH値が12を超える状態が確保されて可塑状、マヨネーズ状、糊状ないしはスラリー状に調製されている混和物である。  The fluidity activated admixture prepared in the blending step in the series of working steps of the reforming treatment method of the present invention is 100 masses of the heat history silicate present in the original position or the carry-in position as the material to be treated based on the dry matter. 2 to less than 20 parts by mass of the modification treatment agent on a dry matter basis, and if necessary, a function-imparting agent is added in an amount of 400 parts by mass or less to obtain an activated admixture. An aqueous solvent is added so that the moisture content of the water content in the activated admixture is ensured to be in the range of 35 to 70% by mass, the amount is adjusted and mixed, and the activated admixture is brought to room temperature. It is an admixture prepared in a plastic, mayonnaise, pasty or slurry form with a pH value exceeding 12 for 3 hours.

応用対象基材
本発明の基材付着型の活用方法において好適に採択される応用対象基材は、無機質材質、岩石・粘土材質、水和鉱物材質、セラミックス・窯業材質、金属材質、木材質、繊維材質、有機質材質ないしはこれら材質の複合材質からなる粉粒体、吸着性粉粒体、砂粒体、顆粒体、造粒体、硬化・固化体、構造体、床体、柱状体、管状体、線状体、板状体、膜状体、ガラクタ体ないしは形状化体等から適宜本発明の目的・用途に応じて選ぶことができる。
Application target substrate The application target substrate suitably adopted in the method of utilizing the substrate adhesion type of the present invention is an inorganic material, rock / clay material, hydrated mineral material, ceramics / ceramic material, metal material, wood quality, Fiber material, organic material or composite material of these materials, adsorptive powder, sand, granule, granulated, hardened / solidified, structure, floor, columnar, tubular, A linear body, a plate-like body, a film-like body, a junk body or a shaped body can be appropriately selected according to the purpose and use of the present invention.

上記の活性化混和物を基材付着型の付着化処理物に加工処理する加工工程は、予め調製された流動性活性化混和物を応用対象基材の表面に所定量の割合で展延、固結、結着、付着、被覆、積層、集合または注入からなる加工手段により目的・用途に応じた応用対象基材と一体化された基材付着型の活性粉体結着物、基材積層複合物、顆粒群体集合物ないしは注充填一体化物からなる付着化処理物とする工程である。  The processing step of processing the activated admixture into a substrate-adhesive-type adhering treatment product is performed by spreading a fluidly activated admixture prepared in advance on the surface of the application target substrate in a predetermined amount ratio, Substrate-attached active powder binder integrated with base material for application according to purpose and application by processing means consisting of consolidation, binding, adhesion, coating, lamination, assembly or injection This is a process for preparing an adhesion-treated product consisting of a product, a granule aggregate, or an injection-filled integrated product.

さらに本発明の基材付着型結着形状体とする一連の作業工程における養生工程は、上記の加工工程で調製された付着化処理物形状化処理物を常温から100℃範囲にある常圧、加圧、減圧条件下における気中、水中、海中、土中、溶液中、蒸気中、非酸素ガス中の雰囲気の群より選ばれる単独雰囲気中ないし2種以上の組み合わせの多段雰囲気中に少なくとも15分間解放して反応・養生を進行して結着硬化の完了している基材付着型の活性粉体結着品、基材積層複合品、顆粒群体集合品ないしは注充填一体化品からなる応用対象基材と一体化された結着形状体とする工程である。  Furthermore, the curing process in a series of work steps to make the substrate adhesion type binding shape body of the present invention is a normal pressure in the range from room temperature to 100 ° C. the adhesion treatment product shaped treatment prepared in the above processing step, At least 15 in a single atmosphere or a multistage atmosphere of a combination of two or more selected from the group of atmospheres in air, water, sea, soil, solution, steam, and non-oxygen gas under pressurized and decompressed conditions Applications consisting of substrate-adhesive active powder binders, substrate-laminated composites, granule aggregate assemblies, or injection-filled integrated products that have been released for a minute and have undergone reaction / curing to complete binding and curing This is a step of forming a bound shape integrated with the target substrate.

したがって、本発明の改質処理方法は、熱履歴シリケートを改質対象素材として、上記の一連の作業工程に付して調製される流動性活性化混和物のアルカリ性成分を固定化せしめてpH10未満が確保され、該改質対象素材に有害物質が共存するときは該有害物質を固定・不溶化する無害化処理を施し、同時に粉粒体の熱履歴シリケートを耐水性で水中再泥化しない形状化処理を施して、自己完結型の結着形状体への改質処理、ないしは応用対象基材と一体化された基材付着型の結着形状体への改質処理を可能とする改質処理方法が提供される。  Therefore, the reforming treatment method of the present invention uses a heat history silicate as a material to be reformed, immobilizes the alkaline component of the fluid activated admixture prepared by the above-described series of work steps, and has a pH of less than 10. When a harmful substance coexists in the material to be modified, a detoxification treatment is performed to fix and insolubilize the harmful substance, and at the same time, the heat history silicate of the granular material is made water-resistant and not re-mudged in water Treatment to improve the self-contained binding shape body, or to modify the base adhesion type binding shape body integrated with the application target base material A method is provided.

一般に、本発明改質処理方法における一連の作業工程を構成する混和工程は、改質対象素材が存在する原位置または持込位置において、休眠成分であるケイ酸塩化合物を主成分とする熱履歴シリケートの粉粒体または含水体からなる改質対象素材に対して、水系溶媒を介して遊離のイオン性ナトリウムが確保されてpH値12を超える改質処理剤、必要に応じて機能付与剤を加え混和して活性化混和物とする工程である。  In general, the mixing process that constitutes a series of work steps in the reforming treatment method of the present invention is a heat history mainly composed of a silicate compound that is a dormant component at the original position or the carry-in position where the material to be modified exists. For the material to be modified consisting of a silicate granular material or a hydrous material, a modification treatment agent in which free ionic sodium is secured via an aqueous solvent and has a pH value of 12 or more, if necessary, a function-imparting agent It is a process of adding and mixing to make an activated mixture.

次いで一連の作業工程を構成する加工工程は、必要に応じて活性化混和物を各種の形状化処理手段・方法により形状化処理物とする加工工程、もしくは予め用意された応用対象基材に付着・結着・被覆・一体化せしめて応用対象基材と一体化された付着化処理物とする加工工程である。  Next, the processing steps constituting a series of work steps are applied to the application target substrate prepared in advance, or the processing step of converting the activated admixture into a shaped processed product by various shaping processing means and methods as necessary. -It is a processing step to make an adhesion treated product integrated with the base material to be applied by binding, covering and integrating.

次いで一連の作業工程を構成する養生工程は、上記の活性化混和物または形状化処理物や付着化処理物を少なくとも常温雰囲気中に解放して反応・養生する養生工程の3工程を基本とする一連の作業工程に付することにより、活性化混和物のアルカリ性成分を固定化してpH10未満が確保され、該改質対象素材に有害物質が共存するときは該有害物質を固定・不溶化する無害化処理を施し、同時に粉粒体の熱履歴シリケートを耐水性で水中再泥化しない形状化処理を施して自己完結型ないしは基材付着型の結着形状体である再資源化資材に改質処理する工程である。  Next, the curing process that constitutes a series of work processes is based on the three processes of the curing process in which the activated admixture, the shaped processed product, or the attached processed product is released to at least a normal temperature atmosphere to react and cure. By applying a series of work steps, the alkaline component of the activated admixture is fixed to ensure a pH of less than 10, and when harmful substances coexist in the material to be modified, the harmful substances are fixed and insolubilized. At the same time, the heat history silicate of the granular material is shaped to be water-resistant and not re-mudged in water, and reformed into a recycled material that is a self-contained or base-attached binding shape It is a process to do.

本発明技術で調製される活性化混和物は、熱履歴シリケートにpH値12を超える改質処理剤、必要に応じて機能付与剤と水系溶媒を加えて調製されるが、本発明の目的・用途、さらに作業性等に応じて、補足成分である機能付与剤を付加・補足して、それぞれの分野からのニーズに応える必要がある。これらの補足成分である機能付与剤は、予め改質処理剤に加えたワンパック化されて採択されることにより一括して活性化混和物とすることもできるが、混和工程において、予め改質処理剤のみを採択して活性化混和物を調製し、次いでこの活性化混和物に機能付与剤を加えて混和する多段式にて複合された混和物を調製することもできる。  The activated admixture prepared by the technique of the present invention is prepared by adding a heat treating silicate with a modifying agent having a pH value exceeding 12 and, if necessary, a function-imparting agent and an aqueous solvent. It is necessary to add / supplement a function-imparting agent as a supplementary component according to the use and workability, and to meet the needs from each field. The function-imparting agent, which is a supplementary component, can be made into an activated admixture as a whole by adopting it as a one-pack in addition to the modifying treatment agent in advance. It is also possible to prepare an activated admixture by adopting only the treatment agent, and then prepare a multi-stage compounded admixture in which a function-imparting agent is added to the activated admixture and mixed.

さらに本発明における改質処理方法においては、熱履歴シリケートと水系溶媒に改質処理剤、必要に応じて機能付与剤を加えて混和して調製される活性化混和物自身を形状化処理する加工工程による形状化処理物を養生工程に付する改質処理方法、さらに該活性化混和物を予め用意された応用対象基材に付着せしめる加工工程による付着化処理物を養生工程に付する改質処理方法の2種類の改質処理方法を挙げることができる。  Further, in the modification treatment method of the present invention, the processing for shaping the activated admixture itself prepared by adding the modification treatment agent and, if necessary, the function-imparting agent to the heat history silicate and the aqueous solvent, is performed. A modification treatment method for subjecting a shaped treatment product to a curing process, and a modification treatment for subjecting an adhesion treatment product to a curing step by a processing step for adhering the activated admixture to a substrate to be applied prepared in advance. There are two types of modification treatment methods.

本発明一連の作業工程における基本的混和工程は、本発明改質対象素材を乾燥物基準で表して100質量部に対して、遊離のイオン性ナトリウムが確保されてpH値12を超える改質処理剤を2ないしは20質量部未満を加え、さらに必要に応じてサプリメント、インプルーブメント、ファンクションメントもしくはレインホースメントで構成される機能付与剤の単独ないし複数からなる機能付与剤を400質量部以下の量で加え、もしくは一括方式により改質処理剤と機能付与剤がワンパック化されて加え、さらに必要に応じて水系溶媒を加えて含水率が10ないし70質量%範囲に確保される状態において常温で3時間を超えない範囲でpH値12が確保されて均質に混和し、バサバサ状、可塑状、マヨネーズ状、糊状ないしスラリー状の混和物を調製する工程である。  The basic mixing step in the series of work steps of the present invention is a reforming treatment in which free ionic sodium is secured and the pH value exceeds 12 with respect to 100 parts by mass of the material to be modified according to the present invention on a dry matter basis. 2 or less than 20 parts by weight of the agent, and if necessary, the amount of the function-imparting agent composed of one or more of the function-imparting agents composed of supplement, improvement, functionment or rain reinforcement is 400 parts by mass or less. In addition, or the reforming agent and the function-imparting agent are added in one pack by a batch method, and an aqueous solvent is added as necessary to maintain the moisture content in the range of 10 to 70% by mass at room temperature. A pH value of 12 is ensured in a range not exceeding 3 hours, and the mixture is homogeneously mixed, with a frustration, plastic, mayonnaise, paste or slurry. A step of preparing a blend.

本発明混和工程で重要なことは、本発明の休眠成分で構成される改質対象素材を乾燥物基準で表して100質量部に対して、遊離のイオン性ナトリウムが確保されてpH値12を超える改質処理剤を2ないし20質量部未満の量で加えて均質な活性化混和物を調製するところにある。このとき加える改質処理剤の量割合が2質量部より少ない時は、本発明改質処理に必要な活性なシリカならびにアルミナを得ることができない。また、加える改質処理剤の量割合が20質量部を超える時は、混和物系内におけるアルカリ成分が多く、活性化後の混和物に遊離のイオン性ナトリウムを過剰に残すことになり、続いて起こる有害元素群の固定化条件を阻害する傾向があり注意が必要である。  What is important in the blending process of the present invention is that the material to be modified composed of the dormant component of the present invention is expressed on a dry matter basis, and free ionic sodium is secured for 100 parts by mass, so that the pH value is 12. More than 2 to less than 20 parts by weight of the modifier is added to prepare a homogeneous activated blend. If the amount of the modifying agent added at this time is less than 2 parts by mass, the active silica and alumina necessary for the modifying treatment of the present invention cannot be obtained. Moreover, when the amount ratio of the modifying treatment agent to be added exceeds 20 parts by mass, there are many alkali components in the mixture system, and excessive ionic sodium is left in the mixture after activation. It is necessary to be careful because it tends to hinder the immobilization conditions of harmful element groups.

本発明の混和工程において調製される活性化混和物の性状は、材料が包含している水分量ないしは同時に加えられる水系溶媒の加える量により異なるが、本発明の目的・用途に応じてそれぞれバサバサ状、可塑状、マヨネーズ状、流動状ないしは分散状からなる活性化混和物に調製することができる。また勿論、改質対象素材の組成内容ならびに熱履歴の受け方、さらに熱履歴を受けてからの経過等により、同じ改質処理剤でも異なる活性化混和物状態を示すことから充分注意して、必要に応じて予備実験により混和工程における混和条件等を確認して施工する必要がある。  The properties of the activated admixture prepared in the blending process of the present invention vary depending on the amount of water contained in the material or the amount of aqueous solvent added at the same time. It can be prepared into an activated admixture consisting of plastic, mayonnaise, fluid or dispersion. Of course, it is necessary to pay close attention to the fact that the same modification treatment agent shows different activated admixture states depending on the composition content of the material to be modified, how to receive the heat history, and the process after receiving the heat history. Therefore, it is necessary to confirm the mixing conditions in the mixing process by a preliminary experiment.

本発明混和工程において、活性化混和物が常温において少なくとも3時間の間混和・放置すると活性化混和物の初期pH値が12を越える高い値から、アルカリ性成分とケイ酸塩系化合物等からなる休眠成分との活性化反応により、混和物のpH値は12を切って低くなる現象から活性化反応の進捗状況を確認することができる。また、活性化混和物調製時の3時間を経過した中での活性化混和物のpH値が12より高い状態であるときは、このpH値の高い状態の活性化混和物では次の工程である養生工程に持ち込んで反応・養生を進めても有害元素群の固定・不溶化を完成することは困難な傾向にあり、注意が必要である。  In the mixing step of the present invention, when the activated admixture is mixed and allowed to stand at room temperature for at least 3 hours, the initial pH value of the activated admixture exceeds 12 from the high value, and a dormancy composed of an alkaline component and a silicate compound, etc. The progress of the activation reaction can be confirmed from the phenomenon that the pH value of the admixture drops below 12 due to the activation reaction with the components. When the pH value of the activated admixture is higher than 12 after 3 hours from the preparation of the activated admixture, the activated admixture with the higher pH value is used in the next step. It is difficult to complete the fixation and insolubilization of harmful elements even if they are brought into a certain curing process and proceed with reaction and curing.

多段
さらに本発明混和工程では、改質対象素材に改質処理剤を予め加えた活性化混和物に対して目的・用途に応じて、補足成分である機能付与剤を追加して加えた活性化混和物を調製することができる。このときの補足成分類の活性化混和物への配合量は、乾燥物基準で表して改質対象素材100質量部に対して、目的・用途・作業性等に応じて機能付与剤を400質量部以下の量で加えることが好ましい。勿論、このとき採択する機能付与剤の種類と組み合わせ、ならびに目的・用途、さらに作業性等に応じて大きく異なることから、予め行う予備実験により配合条件等を決定することが好ましい。
Multi-stage In addition, in the blending process of the present invention, activation is performed by adding a function-imparting agent, which is a supplementary component, to the activated blend obtained by adding a modification treatment agent to the material to be modified in advance according to the purpose and application. An admixture can be prepared. The amount of supplemental components added to the activated admixture at this time is 400 masses of the function-imparting agent according to the purpose, application, workability, etc. with respect to 100 mass parts of the material to be modified, expressed on a dry matter basis. It is preferable to add in an amount of no more than parts. Of course, since it varies greatly depending on the type and combination of the function-imparting agents to be adopted at this time, the purpose / use, and workability, it is preferable to determine the blending conditions and the like through preliminary experiments conducted in advance.

また本発明混和工程においては、改質対象素材に改質処理剤を加えた活性化混和物を常温にて少なくとも3時間の間で混和・放置する条件は、3時間連続して混和手段を継続することも可能であるが、改質対象素材に改質処理剤を加えた活性化混和物が均質状態であることが確認された後は、混和手段を止めて常温中に単に放置することによっても活性化作用は継続され、本発明の目的に適う混和工程を完了することができる。  In the blending process of the present invention, the condition of mixing and leaving the activated blend obtained by adding the modifying treatment agent to the material to be modified at room temperature for at least 3 hours is continued for 3 hours continuously. However, after it has been confirmed that the activated admixture obtained by adding the modifying agent to the material to be modified is in a homogeneous state, the mixing means is stopped and the mixture is simply left at room temperature. However, the activating action is continued and the mixing step suitable for the purpose of the present invention can be completed.

本発明の混和工程において活性化混和物を調製する一般的な混和手段としては、一連の作業工程を実施する場所ならびに作業条件、また目的・用途等により異なるが、一般には当業界(食品業界、化学工業界、窯業工業界、土木・建築業界、農業土木界等)で公知・公用されている混合機、混練機、攪拌機、掘削機、混ぜ機、反応機、分散機、スタビライザー、地盤改良装置、セメント類固化材の混合機、農業用耕運機等の均質混和を可能とする装置類、例えばセメントミルクやコンクリート・窯業製品等の二次製品等の加工現場で採択され混和・混練装置(ミキサー、混合機、混練機等)等を適宜採択・稼動して、本発明の各混和物を好適に回収することができる。  The general mixing means for preparing the activated admixture in the mixing step of the present invention varies depending on the place where the series of working steps are carried out, the working conditions, the purpose and use, etc., but generally this industry (food industry, (Chemical industry, ceramic industry, civil engineering / architecture industry, agricultural and civil engineering industry, etc.) known and publicly used mixers, kneaders, agitators, excavators, mixers, reactors, dispersers, stabilizers, ground improvement devices Adopted at the processing site of secondary products such as cement milk, concrete and ceramic products, etc., which are capable of homogeneous mixing such as cement solidifying material mixers, agricultural cultivators, etc. Each admixture of the present invention can be suitably recovered by appropriately adopting and operating a mixer, a kneader or the like.

特に、改質対象素材の存在する原位置で混和工程を行う場合は、有害物質共存の含水土質・汚泥または砂質土・粘土・岩石の土壌地盤等からなる改質対象素材の存在する原位置に搬入した、土木・建築業界で汎用され公知・公用の混和・混練装置、特に軟弱地盤等の地盤改良現場で汎用されている掘削・混合装置類、地中へのセメント等の混合・注入機等で実績のある装置を好適に採択することができる。例えば、軟弱地盤改良等で採択される工法により粉末またはスラリー状の改質処理剤を地盤深層部に高圧下に注入攪拌する方法、既存の地盤改良工法等による深層混合方法、バックホウ、スタビライザー、自走式土質改良機等の重機類による攪拌混合方式方法等により原位置で混和工程を施すことができる。  In particular, when the mixing process is performed at the site where the material to be reformed is present, the site where the material to be reformed is composed of hydrous soil / sludge or sandy soil / clay / rock soil that coexists with harmful substances. Used in the civil engineering / architecture industry, well-known and publicly used mixing / kneading equipment, especially excavation / mixing equipment used in ground improvement sites such as soft ground, mixing / injecting machine for cement into the ground Thus, it is possible to suitably adopt a device that has a proven record. For example, a method of injecting and stirring a powder or slurry-like modifying agent into the deep ground layer under high pressure by a method adopted for soft ground improvement, etc., a deep layer mixing method using an existing ground improvement method, backhoe, stabilizer, self The mixing process can be performed in-situ by a stirring and mixing method using heavy machinery such as a traveling soil improvement machine.

加工工程
本発明の一連の作業工程において、必要に応じて行われる加工工程は、改質対象素材の存在する原位置にいて、さらには本発明の目的・用途に応じて、上記の混和工程で調製されたバサバサ状、可塑状、マヨネーズ状、糊状ないしはスラリー状にある活性化混和物を土壌地盤、軟弱地盤、道路、堤ないし農地・宅地・公共用地等からなる原位置非成型品、または塊状物、杭状物、農地畦、側溝、道路、堤ないし構造物等からなる原位置での形状化処理物からなる形状化処理物に加工する工程である。
Processing Steps In the series of work steps of the present invention, the processing steps performed as necessary are in the original position where the material to be modified exists, and further according to the purpose and application of the present invention, In-situ non-molded product consisting of the soil mixture, soft ground, road, levee or farmland / residential land / public land, etc., with the prepared mixture in the form of rust, plastic, mayonnaise, paste or slurry This is a step of processing into a shaped processed product made of a shaped processed product at an original position made up of a lump, pile, agricultural landfill, gutter, road, bank, or structure.

また本発明の一連の作業工程において、必要に応じて行われる加工工程は、改質対象素材の存在する持込位置にいて、さらには本発明の目的・用途に応じて、上記の混和工程で調製されたバサバサ状、可塑状、マヨネーズ状、糊状ないしはスラリー状にある活性化混和物を粉粒、造粒、成型、展延、固結、結着、付着、被覆、積層、集合または注入等からなる加工手段により、粉粒物、砂粒物、顆粒物、造粒物、硬化・固化物、構造物、管状物、線状物、多孔質体ないしは形状化物等からなる耐水性粉粒体物ないしは形状加工成型物である形状化処理物に加工する工程である。  Further, in the series of work steps of the present invention, the processing steps performed as necessary are in the carry-in position where the material to be modified is present, and further according to the purpose and application of the present invention, Prepared activated admixture in the form of rust, plastic, mayonnaise, paste or slurry is granulated, granulated, molded, spread, consolidated, bonded, adhered, coated, laminated, assembled or injected Water-resistant granular material consisting of granular material, sand granular material, granular material, granulated material, cured / solidified material, structure, tubular material, linear material, porous material or shaped material, etc. Or it is the process processed into the shaping process thing which is a shape processing molding.

さらに本発明の一連の作業工程において、必要に応じて行われる加工工程は、改質対象素材の存在する持込位置にいて、さらには本発明の目的・用途に応じて、上記の混和工程で調製された可塑状、マヨネーズ状、糊状ないしはスラリー状にある流動性活性化混和物を予め用意された応用対象基材の表面上に所定量の割合で展延、固結、結着、付着、被覆、積層、集合または注入等からなる加工手段により目的・用途に応じた応用対象基材と一体化された基材付着型の活性粉体結着物、基材積層複合物、顆粒群体集合物ないしは注充填一体化物である付着化処理物に加工する工程である。  Furthermore, in the series of work steps of the present invention, the processing steps performed as necessary are in the carry-in position where the material to be modified exists, and further according to the purpose and application of the present invention, The prepared plastic, mayonnaise, paste or slurry fluidized activated admixture is spread, consolidated, bound, and adhered in a predetermined amount on the surface of the base material for application prepared in advance. Substrate-attached active powder binders, substrate laminate composites, granule aggregate aggregates that are integrated with application target substrates according to the purpose and application by processing means including coating, lamination, assembly, or injection Or it is the process processed into the adhesion treatment processed material which is an injection filling integrated material.

本発明の改質対象素材が存在する原位置における加工工程は、改質対象素材の存在する原位置における混和工程と同時に地盤表層部ないしは地盤深層部に常圧ないしは高圧下に注入・攪拌する方法、もしくは既存の土木業界における地盤改良工法等で採択されている乾式もしくは湿式による深層部混合方法等により、原位置にて杭、塊状物、畔、側溝、地盤等からなる形状化処理物に加工処理することができる。  The in-situ processing step in which the material to be modified exists in the present invention is a method of injecting and stirring at normal pressure or high pressure in the ground surface layer portion or deep ground portion at the same time as the mixing step in the original location in which the material to be modified exists. Or, processing into a shaped treatment consisting of piles, lump, side, gutter, ground etc. in the original position by dry or wet deep layer mixing method adopted by the existing ground improvement method in the civil engineering industry etc. Can be processed.

また、改質対象素材が存在する持込位置において特定形状の形状化処理物とする加工工程は、混和工程で混和した混和物を硬化体物、固化体物、成型体物、構造体物、膜状のフイルム、不焼成セラミックス物、不焼成レンガ・耐火物・耐熱物・断熱保温物・耐酸物等に加工処理する。加工手段は当業界の食品業界、化学工業界、窯業工業界、土木・建築・建設業界等で公知・公用されている特定形状の型枠に常圧、加圧、減圧において振動、流し込み、押し込み、叩き込み、鋳込み、造粒、噴霧、引抜等で成型する方法・手段等の加工手段から適宜選択して目的に適した形状化処理物とする工程である。  In addition, the processing step to make the shaped processing product of a specific shape at the carry-in position where the material to be modified is present is a cured product, solidified product, molded product, structural product, It is processed into film-like films, unfired ceramics, unfired bricks, refractories, heat-resistant materials, heat insulation and acid-resistant materials. Processing means are vibration, pouring, and pushing at normal pressure, pressurization, and decompression into a form with a specific shape known and used in the food industry, chemical industry, ceramic industry, civil engineering, construction, construction industry, etc. In this step, a shaped product suitable for the purpose is selected by appropriately selecting from processing means such as a method and means for molding by hammering, casting, granulation, spraying, drawing, and the like.

特に膜状のフィルムにおいては、混和工程で調製された糊状ないしは可塑状の流動性混和物を加工工程において基材類もしくは型類の表面に1ないしは20mm厚の膜状、板状、塗膜状もしくはフィルム状の膜状物とし、養生工程において連膜状物を常温ないしは100℃雰囲気中に10分間以上曝露して養生し、基材類もしくは型類の表面からはずして膜状フイルム品である耐水性の結着形状体とすることができる。  In particular, in the case of a film-like film, the paste-like or plastic fluid mixture prepared in the mixing step is formed on the surface of the base material or mold in the processing step by a film-like, plate-like or coating film having a thickness of 1 to 20 mm. In the curing process, the continuous film is exposed to room temperature or 100 ° C atmosphere for 10 minutes or longer, and is removed from the surface of the base material or mold to form a film-like film product. A certain water-resistant binding shape can be obtained.

さらに改質対象素材が存在する持込位置において不特定形状の形状化処理物とする加工工程は、上記の混和物を顆粒体・骨材体・固結吸着体等の粒状造粒物または集合群体とした形状化処理物とすることもできる。不特定形状に形状化する方法・手段は、かきまぜ、吹き上げ、分散、注入等の手段によって当業界公知・公用の転動造粒、押し出し造粒、攪拌造粒、スプレー法造粒、噴霧造粒、パッキング造粒、ペレタイザー等の造粒装置により、1ないしは8mmφ粒径に造粒された顆粒体・骨材体・固結吸着体等の形状化処理物に加工処理する工程である。  Furthermore, the processing step for forming an unspecified shaped shaped processed product at the carry-in position where the material to be modified is present is a granular granulated product or aggregate such as a granule / aggregate / consolidated adsorbent. It can also be set as the shaped processing object made into the group. Methods and means for shaping into an unspecified shape are known in the art by means of stirring, blowing, dispersing, pouring, etc., publicly known rolling granulation, extrusion granulation, stirring granulation, spray granulation, spray granulation And a granulating apparatus such as a packing granulator and a pelletizer, and the like, and processing into a shaped product such as a granule, an aggregate body, and a consolidated adsorbent granulated to a particle diameter of 1 to 8 mmφ.

本発明一連の作業工程における加工工程で採択される加工手段は、混和工程で加工に適う混和物に調整された混和物を新たに加工工程に適した装置に付して加工成型を行うこともできるが、一連の作業工程において例えば顆粒品等の不特定形状化品を処理調製する時は、混和工程における混和・混練装置による混和とで同時に平行して例えば顆粒品等の不特定形状物を調製することもできる。  The processing means adopted in the processing steps in the series of work steps of the present invention may be performed by subjecting the admixture adjusted to the admixture suitable for processing in the mixing step to a new apparatus suitable for the processing step. However, when processing and preparing unspecified shaped products such as granules in a series of work steps, unspecified shapes such as granules are simultaneously processed in parallel with the mixing and kneading apparatus in the mixing step. It can also be prepared.

本発明一連の作業工程における具体的な加工手段としては、改質処理剤の活用処理を行う場所ならびに作業条件、さらに目的・用途等、さらに混和工程との連続性において異なるが、一般には当業界(食品業界、化学工業界、窯業工業界、土木・建築業界、農業土木界等)で公知・公用されている混合・混練・造粒機、攪拌方式造粒機、加圧式造粒・成型機、流し仕込み方式成型機、押し出し式造粒・成型機、パッキング方式造粒・成型機、さらにセメントミルクやコンクリート・窯業製品等の二次製品等の加工現場で採択されている各種造粒・成型機等を適宜採択して稼動することにより、本発明目的・用途に適う特定形状もしくは不特定形状の形状化処理物を調製することができる。  The specific processing means in the series of work steps of the present invention are different in terms of the place where the modification treatment agent is utilized and the working conditions, and the purpose and use, and the continuity with the mixing step. Known and publicly used in the food industry, chemical industry, ceramic industry, civil engineering / architecture industry, agricultural civil engineering industry, etc., mixing / kneading / granulating machines, agitation granulators, pressure granulating / molding machines Various types of granulation and molding that have been adopted in processing sites such as casting preparation molding machines, extrusion granulation and molding machines, packing granulation and molding machines, and secondary products such as cement milk, concrete and ceramic products. By appropriately selecting a machine or the like and operating it, a shaped or unspecified shaped shaped product suitable for the purpose and application of the present invention can be prepared.

応用対象基材
また本発明の加工工程においては、前述してように混和工程で調製された可塑状、マヨネーズ状、糊状ないしはスラリー状の流動性活性化混和物を活用して、予め用意された応用対象基材である無機質材質、岩石・粘土材質、水和鉱物材質、セラミックス・窯業材質、金属材質、木材質、繊維材質、有機質材質ないしはこれら材質の複合材質等からなる粉粒体、吸着性粉粒体、砂粒体、顆粒体、造粒体、硬化・固化体、構造体、床体、柱状体、管状体、線状体、板状体、膜状体、ガラクタ体ないしは形状化体等の基材類表面に該流動性活性化混和物を塗装、接着、付着、結着、被覆、多層塗り、どぶ浸け、まぶし、貼り付け、塗りつけ、吹き付け、流し込み、注入手段等により付着化加工処理されて塗布物、被覆物、付着物、結着物、床状物、積層物、注入一体化物等からなる付着化処理物とすることができる。
Substrate to be applied In addition, in the processing step of the present invention, it is prepared in advance using a fluidized activated admixture in the form of plastic, mayonnaise, paste or slurry prepared in the blending step as described above. Inorganic materials, rock and clay materials, hydrated mineral materials, ceramics and ceramic materials, metal materials, wood materials, fiber materials, organic materials, or composite materials of these materials, adsorption Powder, sand, granule, granulated, hardened / solidified, structure, floor, columnar, tubular, linear, plate, film, galactor or shaped Coating, adhering, adhering, binding, coating, multilayer coating, soaking, gliding, applying, applying, spraying, pouring, pouring, pouring, pouring, etc. on the surface of substrates such as Processed, coated, covered, adhered, bonded It can be set as the adhesion treatment thing which consists of a kimono, a floor-like thing, a laminate, an injection integration thing, etc.

また本発明の加工工程においては、予め用意された応用対象基材に流動性活性化混和物を活用して付着化処理物とする具体的な加工手段としては、改質処理剤の活用処理を行う場所ならびに作業条件、さらに目的・用途等、さらに混和工程との連続性において異なるが、一般には当業界(塗装業界、食品業界、化学工業界、窯業工業界、土木・建築業界、農業土木界等)で公知・公用されている塗装機械装置、付着・結着機械装置、被覆・コーティング機械装置、床調整装置、流し仕込み方式装置等を適宜採択して稼動することにより、本発明目的・用途に適う付着化処理物を調製することができる。  Further, in the processing step of the present invention, as a specific processing means for using the fluidity activated admixture on an application target substrate prepared in advance to obtain an adhering treatment product, a treatment using a modifying treatment agent is performed. Although it differs in continuity with the mixing process, such as the place where it is performed, the working conditions, the purpose and application, etc., generally this industry (painting industry, food industry, chemical industry, ceramic industry, civil engineering / architecture industry, agricultural civil engineering industry) Etc.) by appropriately adopting and operating the painting machine apparatus, adhesion / binding machine apparatus, coating / coating machine apparatus, floor adjustment apparatus, sink preparation system apparatus, etc. that are known and used in Can be prepared.

養生工程
本発明の一連の作業工程において必要に応じて行われる養生工程は、上記の活性化混和物もしくは形状化処理物を常温、もしくは少なくとも反応に必要な水分の確保が可能な100℃の常圧気中、水中、海中、土中、溶液中、蒸気中、非酸素ガス中、減圧気中ないし加圧気中の雰囲気の群より選ばれる単独雰囲気中ないし2種以上の組み合わせの多段雰囲気中に10分間以上解放して、各活性化混和物ないし形状化処理物における反応・養生を進行せしめ、アルカリ性成分を固定化してpH10未満が確保できる無害化処理を施し、同時に粉粒体の熱履歴シリケートを耐水性で水中再泥化のない形状化処理を施した結着形状体として提供できる工程である。
Curing process The curing process performed as necessary in the series of work processes of the present invention is performed at normal temperature of the above-mentioned activated admixture or shaped product, or at least 100 ° C. capable of securing water necessary for the reaction. 10 in a single atmosphere selected from the group of atmospheres under pressure, water, sea, soil, solution, steam, non-oxygen gas, decompressed air or pressurized air, or in a multistage atmosphere of two or more combinations. Release for more than a minute to advance the reaction and curing in each activated admixture or shaped product, immobilize the alkaline components and perform a detoxification treatment that can secure a pH of less than 10, and at the same time, heat history silicate of the granular material This is a process that can be provided as a bound shaped body that is water-resistant and has undergone a shaping process without re-mudging in water.

本発明の混和工程ないしは加工工程で調製された活性化混和物ないしは形状化処理物を養生工程に付して、アルカリ性成分を固定化してpH10未満が確保できる無害化処理が施され、同時に粉粒体の熱履歴シリケートを耐水性で水中再泥化のない形状化処理が施され、粉粒体、砂粒体、顆粒体、硬化・固化体、構造体、形状体、フイルム・膜状体、機能性保有被覆体、積層・塗布体、顆粒群体の集合体ないしは注充填一体化体に形状化処理が施され、自己完結型の原位置非成型品、耐水性粉粒体品、形状加工成型品、さらに基材付着型の活性粉体結着品、基材積層複合品、顆粒群体集合品または注充填一体化品である結着形状体に好適に改質処理することができる。  The activated admixture or shaped product prepared in the blending step or processing step of the present invention is subjected to a curing step, and subjected to a detoxification treatment that can fix the alkaline component to ensure a pH of less than 10, and at the same time, powder particles The body's thermal history silicate is water-resistant and shaped without water re-mudging, so that the powder, sand, granule, cured / solidified, structure, shape, film / film, function Self-contained in-situ non-molded product, water-resistant granular product, and shape-processed molded product. Furthermore, it can be suitably modified to a binder-shaped body which is a base-attached active powder binder, a base-layer composite, a granule aggregate, or an injection-filled integrated product.

本発明の混和工程における活性化混和物が、原位置に持ち込んで施設された処理装置により、原位置に存在して有害物質を共存する汚染土壌地盤の乾燥物基準で100質量部に対して、改質処理剤を5ないし30質量部、さらに汚染土壌地盤が保有している水分を勘案して水系溶媒を少なくとも20質量部以上になるように活性化混和物を原位置で調整し、次いで原位置で混和された活性化混和物に対して加工工程を経ることなく原位置における環境下の常温雰囲気中に少なくとも24時間曝露養生することにより原位置非成型品である土壌地盤、軟弱地盤、道路、堤ないしは農地・宅地・公共用地に無害化処理および形状化処理が施されて結着形状体に改質処理することができる。  The activated admixture in the mixing step of the present invention is brought into place in the in-situ facility, and 100 parts by mass on the basis of the dry matter of the contaminated soil ground that is in-situ and coexists with harmful substances, The activated admixture is adjusted in-situ so that the water content of the modified solvent is 5 to 30 parts by mass and the water-based solvent is at least 20 parts by mass in consideration of the moisture contained in the contaminated soil ground. Soil ground, soft ground, road, which is an in-situ non-molded product, by exposing and curing the activated admixture mixed at the position in a normal temperature atmosphere in the environment at the original position for at least 24 hours without passing through a processing step The embankment or farmland / residential land / public land can be detoxified and shaped to be modified into a bound shape.

さらに、本発明の混和工程における活性化混和物が、原位置に持ち込んで施設された処理装置により、原位置に存在して有害物質を共存する汚染土壌地盤、汚染軟弱地盤、汚染道路・堤ないしは汚染農地・宅地・公共用地の乾燥物基準で100質量部に対して、改質処理剤を5ないし30質量部、さらに汚染土壌地盤が保有している水分を勘案して水系溶媒を少なくとも20質量部以上になるように活性化混和物を原位置で調整し、次いで活性化混和物を塊状物、杭状物、農地畦、側溝、道路、堤ないしは構造物からなる形状化処理物に加工し、次いで原位置で混和・加工された形状化処理物を原位置における環境下の常温雰囲気中に少なくとも24時間曝露養生することにより形状加工成型物である塊状体、杭状体、農地畦、側溝、道路、堤ないし構造体に無害化処理および形状化処理が施されて結着形状体に改質処理することができる。  Furthermore, the activated admixture in the mixing step of the present invention is brought into the original position by the processing equipment installed in the original position, contaminated soil ground, contaminated soft ground, contaminated road / bank or 5 to 30 parts by weight of the modification treatment agent and 100 parts by weight of the dry matter on the contaminated agricultural land / residential land / public land, and at least 20% by weight of the aqueous solvent in consideration of the water content of the contaminated soil ground Adjust the activated admixture in-situ so that it is at least part, and then process the activated admixture into a shaped product consisting of a lump, pile, farmland, gutter, road, levee or structure. Then, the shaped processed material mixed and processed in-situ is exposed and cured in a normal temperature atmosphere in the in-situ environment for at least 24 hours. ,road, Or it can detoxification and shaping process to the structure is subjected to modification treatment in the binder-shaped body.

本発明における養生工程は、常温を含む低温において特別な装置・エネルギー等を必要とせず、また必要に応じて改質対象素材の存在する原位置で養生を行うこともできる。しかし、養生工程の条件は、常温、常圧に限定されず、加圧ないし減圧でも可能である。また雰囲気も、大気中のみならず酸素を絶った窒素雰囲気や、他の不活性ガスや特定ガス中、加湿中、また水系内での条件で常温・加温での養生工程も可能である。さらに、養生工程の雰囲気に赤外線、電磁波・放射線や各種波長を照射することも可能である。  The curing process in the present invention does not require special equipment / energy at a low temperature including normal temperature, and can be cured in situ where the material to be reformed is present, if necessary. However, the conditions of the curing process are not limited to normal temperature and normal pressure, and can be increased or reduced. In addition to the atmosphere, the atmosphere can be a nitrogen atmosphere in which oxygen is cut off, another inert gas, a specific gas, humidification, or a curing process at room temperature and warming in an aqueous system. Furthermore, it is also possible to irradiate the atmosphere of the curing process with infrared rays, electromagnetic waves / radiation and various wavelengths.

また、本発明における養生工程は、特に常温における養生工程においては、気中と水中の多段雰囲気で養生することも可能である。即ち、混和物または形状加工物を常温において少なくとも3時間放置して、初期的反応を経過した後、各種雰囲気である気中(常圧大気中、各種気体による置換雰囲気中等)、溶液中(純水、雨水、水道水、工業用水、海水、河川水、排水、排水処理水、塩類含有溶液等)、土中もしくは気中と溶液中等の多段で組み合わせた雰囲気中により反応・養生を進行・完結させることができる。  Moreover, the curing process in the present invention can be cured in a multistage atmosphere in the air and water, particularly in the curing process at room temperature. That is, the mixture or shaped product is allowed to stand at room temperature for at least 3 hours and after an initial reaction, in various atmospheres (in atmospheric pressure, in a replacement atmosphere with various gases), in solution (pure Water, rainwater, tap water, industrial water, seawater, river water, drainage, wastewater treatment water, salt-containing solutions, etc.), in soil or in a combination of atmospheres and solutions, etc. Can be made.

勿論、養生雰囲気を減圧、加圧、加温、加湿等の条件下で養生することもできる。また、混和物ないし加工形状化物を常温ないしは100℃の気中、非酸素ガス中、水中、海中、土中、溶液中、蒸気中、加温中、減圧中または加圧中の雰囲気の群より選ばれる単独雰囲気中ないしは2種以上の組み合わせの多段雰囲気中に最低10分間曝露して養生することもできる。特に、底質等の水域における処理対象物を再資源化資材に改質するときは、底質等の存在する水域原位置での本発明改質処理剤を活用する一連の作業工程からなる改質方法に付するときは、混和物ないしは混和物の形状化処理物における養生工程を水中で行うことは、養生場所の確保等から好ましい。  Of course, the curing atmosphere can be cured under conditions such as reduced pressure, pressurization, heating, and humidification. In addition, admixtures or processed shaped products can be obtained from a group of atmospheres at normal temperature or 100 ° C. in air, non-oxygen gas, water, sea, soil, solution, steam, warming, decompression, or pressurization. It can also be cured by exposure for a minimum of 10 minutes in a selected single atmosphere or in a multistage atmosphere of a combination of two or more. In particular, when reforming an object to be treated in a water area such as bottom sediment to recyclable material, the reform consists of a series of work steps that utilize the modified treatment agent of the present invention in the water area where the bottom sediment is present. When subjecting to a quality method, it is preferable to perform the curing step in the mixture or the shaped product of the mixture in water from the standpoint of securing the curing site.

但し、本発明の養生工程で所定温度に暴露・放置する時間は、一般的に常温では3時間以上から硬化が始まり、12時間で充分であるが、2日間以上、好むらくは7日間以上、さらに好むらくは28日間以上放置することで反応・養生はほぼ完了する。なお、特殊な活用品によっては、7日を越えてさらに時間を要するケースもあるが、予め行う簡単な実験により、必要とする温度ならびに時間を確認することができる。  However, the time of exposure to the predetermined temperature in the curing process of the present invention is generally 3 hours or more at normal temperature, and 12 hours is sufficient, but 2 days or more, preferably 7 days or more, More preferably, the reaction and curing are almost completed by leaving it to stand for more than 28 days. Although there are cases where it takes more time than 7 days depending on the special utilization product, the required temperature and time can be confirmed by a simple experiment performed in advance.

本発明における養生工程の反応・養生処理条件において、処理温度が常温よりも低いときには、反応・養生の進行に時間を要する。処理温度が40℃を超えて例えば100℃の範囲であっても反応に必要な水を確保できる加圧等に雰囲気で結着形状体の反応・養生を完成させることは可能である。特に生産性が求められる工場生産ラインにおいて生産する場合は、加温下での養生工程の遂行は生産性効率を上げる上で有効である。勿論、100℃以上の処理温度で養生工程を行うことを本発明技術は拒むものではない。  In the reaction / curing treatment conditions of the curing process in the present invention, when the treatment temperature is lower than normal temperature, it takes time to advance the reaction / curing. It is possible to complete the reaction and curing of the bound-shaped body in an atmosphere under a pressure or the like that can secure water necessary for the reaction even if the treatment temperature is in the range of 40 ° C. exceeding 40 ° C. In particular, when producing in a factory production line where productivity is required, performing the curing process under heating is effective in increasing the productivity efficiency. Of course, the technique of the present invention does not refuse to perform the curing process at a treatment temperature of 100 ° C. or higher.

しかし、養生処理温度が100℃を超えると介在している水の蒸発が急激に始まり、本発明の結着形状体形成に必要な水和鉱物の形成を阻害する傾向があり考慮する必要がある。したがって、水分蒸発を抑える手段、例えば密閉・加圧条件下や蒸発を物理的に抑える手段を併用して高温での養生工程を行うことは有効とする。勿論、本発明においては、100℃を超える温度を密閉・加圧条件下等で形成せしめて養生工程を行うことも可能であり、また直接100℃以上の高温で処理することも可能であり、これら高温での養生肯定を積極的に拒むものではない。  However, if the curing treatment temperature exceeds 100 ° C., the water in the intervening water starts to evaporate rapidly, and there is a tendency to inhibit the formation of the hydrated mineral necessary for the formation of the bound shape body of the present invention. . Therefore, it is effective to perform a curing process at a high temperature in combination with means for suppressing moisture evaporation, for example, a hermetically sealed / pressurized condition or a means for physically suppressing evaporation. Of course, in the present invention, it is possible to carry out the curing process by forming a temperature exceeding 100 ° C. under sealed / pressurized conditions, etc., and it is also possible to directly process at a high temperature of 100 ° C. or higher. It does not actively reject these high-temperature cures.

本発明改質方法における一連の作業工程は、以上示してきたように基本的に特別な熱エネルギーを必要としない常温で遂行することができる。したがって、一連の作業工程に特別な高価な熱エネルギーを必要とする装置の必要はなく、また特別な熱エネルギー消費もなく、また熱エネルギーを使用したことにより発生する排気処理の必要もなく、資源問題ならびに環境問題等に余分な負担をかけることなく、経済的に廃棄物類を無公害型の再資源化資材として、安全にして安価に供給できることが理解される。  As described above, a series of work steps in the reforming method of the present invention can basically be performed at room temperature that does not require special heat energy. Therefore, there is no need for equipment that requires special expensive heat energy for a series of work processes, no special heat energy consumption, no exhaust treatment that occurs due to the use of heat energy, It is understood that waste can be safely and inexpensively supplied as a pollution-free recycling material without placing an extra burden on problems and environmental problems.

[機能付与剤]
本発明の機能付与剤は、上記した改質処理剤に対して本発明の目的・用途に応じて各種の機能・性状・物性が求められて製品が多様化するために多様な機能性を付加・補足し、一連の作業工程も原位置あり、持込位置における作業性の効率を向上、ならびに改質処理された結着形状体に求められる物性・性状の発揮を可能とする化合物ないし組成物であるサプリメント(補充・補足組成物等)、インプルーブメント(作業改善・向上組成物等)、ファンクションメント(機能性付与組成物)またはレインホースメント(粗骨材、骨材質組成物、繊維質組成物)の単独ないし2種以上の組み合わせの粉粒体ないしは不特定形状体で構成され、必要に応じてワンパック化されていることが好ましい。
[Functional imparting agent]
The function-imparting agent of the present invention adds various functionalities to the above-mentioned modifying treatment agent in order to diversify products because various functions, properties and physical properties are required according to the purpose and application of the present invention.・ Complementary compounds or compositions that have a series of work steps in place, improve workability efficiency at the carry-in position, and exhibit the physical properties and properties required for the modified shaped binding body Supplements (replenishment / supplemental composition, etc.), improvement (work improvement / enhancement composition, etc.), functionment (functionality-imparting composition) or rain reinforcement (coarse aggregate, bone material composition, fiber composition) 1) or a combination of two or more kinds of powders or unspecified shapes, and it is preferable that they are made into one pack if necessary.

勿論、本発明の機能付与剤は、本発明の一連の作業工程における混和工程において、多段に分割してそれぞれ配合することもできる。しかし、予め乾燥物基準で改質処理剤100質量部に対して、サプリメント、インプルーブメント、ファンクションメントないしはレインホースメントの機能付与剤の単独ないし複数からなる機能付与剤を400質量部以下の量で付加されて必要な改質処理剤と均質混合されてワンパック品として扱うこともできる。  Of course, the function-imparting agent of the present invention can be blended in multiple stages in the mixing step in the series of working steps of the present invention. However, with respect to 100 parts by mass of the modified treatment agent in advance on a dry matter basis, a function-imparting agent consisting of one or more of a function-imparting agent for supplements, improvements, functionments or rain reinforcements in an amount of 400 parts by mass or less. In addition, it can be treated as a one-pack product by being homogeneously mixed with the necessary modifying treatment agent.

また、本発明の改質処理剤は、基本的には固形体である粉粒体であることが好ましいが、添加して調製される活性化混和物が水を介して調製されることから、活性化混和物に必要な水配合量の範囲内で予め水に分散ないしは溶解して包含担持している液状体で取り扱うことも一向に構わない。  In addition, the modifying treatment agent of the present invention is preferably basically a solid powder, but since the activated admixture prepared by addition is prepared through water, It may be handled in a liquid form that is dispersed or dissolved in water in advance within the range of the amount of water necessary for the activated admixture.

サプリメント
本発明の改質処理剤を構成する機能付与剤であるサプリメントとしては、主として本発明活性化活用成分を補充し、結着形状体に多様の機能性を付与する化合物ないしは組成物であり、アルカリ金属塩ないしアルカリ土類金属塩の化合物を主成分とするアルカリ補充組成物、硫黄のオキシ酸化合物ないしは硫化物を主成分とする硫黄含有組成物、2価ないしは3価の鉄化合物である鉄塩補充組成物、親油性で活性なフェロケイ酸塩組成物もしくはシラノール基含有組成物であるケイ酸塩補充組成物の群より選ばれる単独ないし2種以上の組み合わせで構成される粉粒体を好適に挙げることができる。
Supplement As a supplement that is a function-imparting agent constituting the modifying treatment agent of the present invention, it is a compound or composition that mainly supplements the activation utilization component of the present invention and imparts various functions to the bound shape body, Alkali replenishment composition mainly composed of alkali metal salt or alkaline earth metal salt compound, sulfur-containing composition mainly composed of sulfur oxyacid compound or sulfide, iron which is divalent or trivalent iron compound Preferred is a powder composed of a single or a combination of two or more selected from the group of a salt replenishment composition, a lipophilic and active ferrosilicate composition, or a silanol group-containing composition. Can be listed.

特に、補充・機能付与剤であるサプリメントが、本発明改質処理剤として仕様の完成されている活性化活用成分からなる粉粒体に対して、本発明の目的・用途・作業性・環境に応じた特注品として本発明改質処理剤が調製されるときは、その目的・用途・作業性・環境に応じて改質処理剤に準じた内容で組成内容の変更された組成成分が添加配合されて改質処理剤を補足する必要がある。これらの補足するサプリメントは、複合粉粒体として均質にワンパック化されていることが好ましいが、目的・用途・作業性等に応じて、必要な機能付与剤を本発明改質処理剤の採択活用される作業現場で、基礎配合の改質処理剤に計り込み配合することも可能である。  In particular, the supplement, which is a replenishment / function-imparting agent, has the purpose, application, workability, and environment of the present invention with respect to the granular material composed of the activated utilization component whose specifications are completed as the present modification treatment agent. When the modified treatment agent of the present invention is prepared as a custom-made product, a composition component whose composition content has been changed according to the purpose, application, workability, and environment is added and blended. Need to be supplemented with the modifying agent. These supplements are preferably uniformly packed as a composite powder, but depending on the purpose, application, workability, etc., the necessary function-imparting agent is selected as the present modification treatment agent. It is also possible to measure and blend into the basic blending modification agent at the work site to be utilized.

本発明のサプリメントであるアルカリ補充組成物としては、本発明の目的・用途・環境に応じて、本発明改質処理剤の改質処理剤としてアルカリ成分がさらに必要なときに補充するアルカリ成分であって、改質処理剤の活性化活用成分として選択されるナトリウム含有成分以外のアルカリ成分を適宜選択して好適に採択することができる。  As an alkali replenishment composition that is a supplement of the present invention, an alkali component to be replenished when an alkali component is further required as a modification treatment agent of the present modification treatment agent, depending on the purpose, use, and environment of the present invention. Thus, an alkali component other than the sodium-containing component selected as the activation utilization component of the modifying treatment agent can be appropriately selected and suitably adopted.

本発明サプリメントのアルカリ補充組成物であるアルカリ成分は、下記組成式(7)

Figure 2006247645
[式中:Mはアルカリ金属元素、MIIはアルカリ土類金属元素、aならびにbは1ないし10の数、wは零を含む12以下の数]で表されるアルカリ金属もしくはアルカリ土類金属の酸化物の群より選ばれる単独ないし2種以上の組み合わせのアルカリ性成分を伴っている粉粒体もしくは含ナトルウム休眠成分を伴う廃棄物類を好適に挙げることができるである。The alkali component which is the alkali replenishment composition of the supplement of the present invention has the following composition formula (7):
Figure 2006247645
[In the formula: M I is an alkali metal element, M II is an alkaline earth metal element, a and b are 1 to 10 and w is a number of 12 or less including zero] Preferred examples include powders with a single or a combination of two or more alkaline components selected from the group of metal oxides or wastes with a sodium-containing dormant component.

本発明改質処理剤に伴われるカルシウム塩組成物としては、下記組成式(2)

Figure 2006247645
[式中;Tはアルミニウム、ケイ素、窒素、硫黄、炭素、ホウ素、リン元素群の単独ないし2種以上の組み合わせ元素、Xはハロゲン元素、a、b、cは零を含む10以下の数、mは0.5ないし6の数、wは零を含む28以下の数]で表されるカルシウムのオキシ酸塩ないしはハロゲン塩化合物の群より選ばれる単独ないし2種以上の組み合わせの正塩、塩基性塩、酸性塩もしくは酸化性塩の化合物から選択することができる。As a calcium salt composition accompanying the present modification treatment agent, the following composition formula (2)
Figure 2006247645
[Wherein, T is an aluminum, silicon, nitrogen, sulfur, carbon, boron, phosphorus element group alone or a combination of two or more elements, X is a halogen element, a, b, c are 10 or less numbers including zero, m is a number of 0.5 to 6, w is a number of 28 or less including zero], or a normal salt or base selected from the group of calcium oxyacid salts or halogen salt compounds It can be selected from a compound of an acidic salt, acidic salt or oxidizing salt.

本発明改質処理剤に伴われる含カルシウム休眠成分を補足する廃棄物組成物としては、廃棄される石灰中和スラッジ、副生・廃石こうボードの廃石こう、高炉や製鋼のスラグおよび保温・断熱材の廃ケイ酸カルシウムの群より選ばれる単独ないし2種以上の組み合わせカルシウム塩化合物を主成分とする廃棄物類から選択することができる。  The waste composition supplementing the calcium-containing dormant component accompanying the modified treatment agent of the present invention includes waste lime neutralized sludge, waste gypsum of byproduct / waste gypsum board, slag of blast furnace and steel making, and heat insulation / heat insulation. It can be selected from wastes mainly composed of a single or two or more combined calcium salt compounds selected from the group of waste calcium silicate.

また、本発明改質処理剤に伴われるカルシヤ含有鉱物組成物としては、ポルトランドセメント、混合セメント(高炉セメント、フライアッシュセメント等)、特殊セメント白色セメント、アルミナセメント、超速硬性セメント、コロイド状セメント、油井セメント、地熱セメント、膨潤セメント、カルシウム鉱物類の群より選ばれる単独ないし2種以上の組み合わせからなるセメント鉱物類から選択することができる。  Further, as the mineral-containing mineral composition accompanying the modifying agent of the present invention, Portland cement, mixed cement (blast furnace cement, fly ash cement, etc.), special cement white cement, alumina cement, super fast setting cement, colloidal cement, It can be selected from cement minerals consisting of a single or a combination of two or more selected from the group of oil well cement, geothermal cement, swelling cement and calcium minerals.

また、本発明改質処理剤に伴われる炭カル変性組成物としては、炭酸カルシウムを主成分とする炭酸カルシウム類100質量部に対して、塩酸、硫酸、亜硫酸、硝酸、亜硝酸、ケイ酸、アルミのケイ酸、アルミン酸、ホウ酸ならびにリン酸の群により選ばれる単独ないし2種以上の組み合わせの酸根を50質量部加えて980℃以下で熱処理して脱炭酸されている炭カル変性組成物から選択することができる。  In addition, as the carbonized cal-modifying composition accompanying the present modification treatment agent, hydrochloric acid, sulfuric acid, sulfurous acid, nitric acid, nitrous acid, silicic acid, with respect to 100 parts by mass of calcium carbonate containing calcium carbonate as a main component, Carbonaceous cal-modified composition which is decarboxylated by adding 50 parts by mass of an acid radical selected from the group consisting of silicic acid, aluminate, boric acid and phosphoric acid of aluminum and heat-treating it at 980 ° C. or lower. You can choose from.

カルシヤ成分として選択される炭カル変性組成物の具体的な例は、炭酸カルシウムを主成分とする天然の霰石、方解石、大理石、貝殻等100質量部に対して、塩酸、硫酸、亜硫酸、硝酸、亜硝酸、ケイ酸、アルミノケイ酸、アルミン酸、ホウ酸ならびにリン酸の群より選ばれる単独ないし2種以上の組み合わせの酸根を少なくとも30質量部加えて、1000℃を超えない範囲で熱処理して脱炭酸処理により調製することができる。  Specific examples of the char modified composition selected as the calcium component include hydrochloric acid, sulfuric acid, sulfurous acid, nitric acid, 100 parts by mass of natural aragonite, calcite, marble, shells and the like mainly composed of calcium carbonate. Add at least 30 parts by mass of an acid radical of one or a combination of two or more selected from the group of nitrous acid, silicic acid, aluminosilicic acid, aluminate, boric acid and phosphoric acid, and heat-treat in a range not exceeding 1000 ° C. It can be prepared by carbonic acid treatment.

特に、ホタテや牡蠣等の貝殻は、カルシウム成分原料としての宝庫である。しかし、貝殻は炭酸カルシウムが主成分であることから有効利用されずに放置され処分に窮している。この貝殻を本発明の混合原料の原料として採択することは、貝殻の再利用につながり有効である。しかも、貝殻を原料として海底ドロ等の固化再資源化に応用することは、処理処分せねばならない廃棄物(ヘドロ等)を海産物の廃棄物を利用して再資源化して、海の環境を改善できることは大変好ましい。  In particular, shells such as scallops and oysters are a treasure trove as a calcium component raw material. However, since the shell is mainly composed of calcium carbonate, it is left unusable and disposed of. Adopting this shell as a raw material of the mixed raw material of the present invention is effective in reusing the shell. Moreover, applying shellfish as raw material to solidify and recycle seabed waste, etc., improves the marine environment by recycling waste that must be disposed of (such as sludge) using seafood waste. It is very preferable to be able to do it.

本発明のサプリメントである鉄塩補充組成物は、特に重金属類を共存している改質対象素材において、重金属類のゼオライト化を容易にし、重金属類の不溶化を促進するために本発明改質処理剤の機能付与剤として好適である。特に砒素やクロムに対しては、鉄塩粉状体を共存せしめておくことにより重金属類の固定・不溶化が有効に発揮され、無害化処理を完結させる上で好ましい。  The iron salt replenishment composition that is a supplement of the present invention is a modification process of the present invention in order to facilitate the formation of heavy metals into zeolite and promote the insolubilization of heavy metals, particularly in materials to be reformed that coexist with heavy metals. It is suitable as a function-imparting agent. In particular, arsenic and chromium are preferably used in the presence of an iron salt powder to effectively fix and insolubilize heavy metals and complete the detoxification treatment.

本発明のサプリメントである硫黄含有組成物としては、本発明改質処理剤の活性化活用成分の構成成分として選んだ硫黄含有成分である芒硝型組成物もしくは明礬型組成物、さらに硫化物含有組成物を補充する成分として適宜選択することができ、さらにカルシウム塩である石こう型組成物を適宜選択することができる。  As the sulfur-containing composition that is the supplement of the present invention, a sulfur-containing composition or alum-type composition that is a sulfur-containing component selected as a component of the activation utilization component of the present modification treatment agent, and a sulfide-containing composition As a component for supplementing the product, a gypsum-type composition that is a calcium salt can be selected as appropriate.

本発明のサルファリメントである石こう型組成物は、硫酸根含有の化合物または組成物類であって、下記組成式(8)

Figure 2006247645
[式中:Zはアルカリ土類金属のカルシウムないしマグネシウム、bは10以下の数、nは2または3の数、wは零を含む2以下の数]で表されるアルカリ土類金属の硫黄のオキシ酸塩の塩基性塩ないし正塩を主成分とする粉粒体を好適に挙げることができる。The gypsum-type composition which is the sulfament of the present invention is a sulfate group-containing compound or composition having the following composition formula (8):
Figure 2006247645
[Wherein Z is calcium or magnesium of an alkaline earth metal, b is a number of 10 or less, n is a number of 2 or 3, and w is a number of 2 or less including zero] Preferable examples include powders mainly composed of basic salts or normal salts of oxyacid salts.

石こう型組成物である硫酸カルシウムは、温度により結晶水が相互転換する2水塩、半水塩、無水塩の7種類が知られている。本発明では、これら石こうも採択が可能であり、効果に大きな差はない。ただ、石こうの入手の容易さから2水塩石こうが一般的である。石こう型組成物の硫酸カルシウムは、リン酸製造ならびに顔料等の酸化チタン(チタン白)の製造の際に副生して処分に窮している廃石こうを好適に選ぶことができる。また、建築業界で多量使用されている石こうボードが建設廃材となる廃石こうボードが乾式で回収されることからサルファリメント原料として好適に採択することができる。  Calcium sulfate, which is a gypsum-type composition, is known in seven types, dihydrate, hemihydrate, and anhydrous salt, in which crystal water interconverts with temperature. In the present invention, these gypsum can also be adopted, and there is no significant difference in effect. However, dihydrate gypsum is common because of the availability of gypsum. As the calcium sulfate of the gypsum-type composition, waste gypsum which is by-produced during the production of phosphoric acid and the production of titanium oxide (titanium white) such as pigments can be suitably selected. In addition, the gypsum board used in large quantities in the construction industry can be suitably adopted as a sulfur raw material because the waste gypsum board used as construction waste is collected in a dry manner.

さらに本発明のサルファリメントとして選ばれる硫化物含有組成物としては、硫化ナトリウム、硫化カルシウム、硫化マグネシウム、硫化アルミニウム、硫化鉄ないしは硫化鉱物の群より選ばれる単独ないし2種以上の組み合わせの粉粒体を好適にあげることができる。この中で硫化ナトリウムは、ナトリウムを含んでいることから、基礎成分のアルカリソルトの成分とすることもできるが、硫化ナトリウムは、空気中で容易に分解して巣酸化ナトリウムに変化することから、特に処理材の水溶出pHへの影響に注意して取り扱う必要がある。硫化物含有組成物としては、天然の硫塩鉱物を含む硫化鉱物である黄鉄鉱、車骨鉱、鶏冠石等をから選びことができる。しかし、これらの硫化鉱物には一般に硫黄に類似したセレン,テルル,砒素,アンチモン,蒼鉛の金属元素、ならびに銀・水銀・銅・鉛・亜鉛・モリブデンの金属元素を共存している場合が多いことから、充分注意して取り扱う必要がある。  Further, the sulfide-containing composition selected as the sulfide of the present invention includes a single or a combination of two or more selected from the group of sodium sulfide, calcium sulfide, magnesium sulfide, aluminum sulfide, iron sulfide or sulfide mineral. Can be preferably mentioned. Among them, sodium sulfide contains sodium, so it can be used as a basic alkali salt component. However, sodium sulfide is easily decomposed in air and converted into nest oxide, In particular, it is necessary to handle with care to the influence of the treatment material on the water elution pH. The sulfide-containing composition can be selected from pyrite, car bone mineral, poultry stone, and the like, which are sulfide minerals containing natural sulfate minerals. However, these sulfide minerals generally contain selenium, tellurium, arsenic, antimony, and lead metal elements similar to sulfur and silver, mercury, copper, lead, zinc, and molybdenum metal elements in many cases. Therefore, it is necessary to handle with great care.

以上示してきた硫酸根保有組成物ならびに硫化物含有組成物は、特別な試作品として、また一般に工業薬品として入手容易であるが、産業界における化学工業界、電力業界、排煙処理業界等から廃棄物や副生物として産・排出されており、安価な廃棄物類のリサイクル品としての活用・利用が有効であり、硫酸根保有組成物ならびに硫化物含有組成物の供給の場は広く、これらの硫酸根保有組成物ならびに硫化物含有組成物類を活用・利用することは、廃棄物のリサイクル利用の立場から好ましい。  The sulfate radical-containing compositions and sulfide-containing compositions shown above are easily available as special prototypes and generally as industrial chemicals, but from the chemical industry, electric power industry, flue gas treatment industry, etc. Produced and discharged as waste and by-products, it is effective to use and use inexpensive recycled products as recycled products, and there are a wide range of supply sites for sulfate radical-containing compositions and sulfide-containing compositions. Utilizing and utilizing the sulfate radical-containing composition and the sulfide-containing composition is preferable from the viewpoint of recycling of waste.

本発明サプリメントである鉄塩補充組成物としては、下記組成式(9)

Figure 2006247645
[式中;Tはアルミニウム、ケイ素、硫黄、窒素、リン元素群の単独ないし2種以上の組み合わせの元素、nは2ないし3の数、mは0.5ないし6の数、wは零を含む28以下の数]で表される鉄の各元素のオキシ塩化合物の群より選ばれる単独ないし2種以上の組み合わせの鉄塩化合物からなる粉粒体を好適に挙げることができる。As an iron salt supplement composition which is the supplement of the present invention, the following composition formula (9)
Figure 2006247645
[Wherein, T is an element of an aluminum, silicon, sulfur, nitrogen, phosphorus element group alone or a combination of two or more, n is a number of 2 to 3, m is a number of 0.5 to 6, and w is zero. Preferred examples include powders composed of a single or a combination of two or more iron salt compounds selected from the group of oxy salt compounds of each element of iron represented by the number of 28 or less.

本発明に好適に採択される鉄塩補充組成物としては、2価または3価の水酸化鉄化合物が特に有効であり、入手容易な面から2価または3価の塩化鉄や硫酸鉄、さらに金属鉄分も好適に挙げることができる。これら金属鉄分、塩化鉄や硫酸鉄は本発明改質処理剤に配合されるカルシヤ組成物と反応して、また大気中の酸素や水分と反応して容易に水酸化鉄化合物を形成し、本発明改質処理剤に求められる作用機能性の一つである重金属類の不溶・固定化する無害化処理における補助的効果を発揮することができる。  As the iron salt supplement composition suitably employed in the present invention, a divalent or trivalent iron hydroxide compound is particularly effective. From the viewpoint of easy availability, divalent or trivalent iron chloride or iron sulfate, Metallic iron can also be preferably cited. These metallic iron, iron chloride and iron sulfate react with the calcium composition blended in the present modification treatment agent, and also react with oxygen and moisture in the atmosphere to easily form an iron hydroxide compound. An auxiliary effect in the detoxification treatment for insolubilizing and immobilizing heavy metals, which is one of the functional functions required for the inventive modification treatment agent, can be exhibited.

本発明のサプリメントである親油性で活性なフェロケイ酸塩組成物としては、熱履歴シリケートの人工合成品における混合原料に選ばれたケイ酸塩組成物である層状粘土鉱物は、アロフェン、ヒシンゲル石、パイロフェライト、タルク、雲母、モンモリロナイト石群、バーミキュル石、リョクデイ石群、カオリナイトもしくはイノケイ酸塩の群より選ばれる単独ないし2種以上の組み合わせのフェロケイ酸塩を好適に挙げることができる。さらに天然または合成のケイ酸塩化合物でウオラストナイト、ゾーノトライトやトバモライトであるケイ酸カルシウムやケイ酸マグネシウム、ケイ石、石英、珪藻土、長石類、沸石、花崗岩・変成岩・流紋岩・礫岩等の岩石鉱物、モルデン石からなるアルミノケイ酸塩鉱物もしくは水ガラスやガラス類のケイ酸アルカリの群から選ばれる単独ないし2種以上の組み合わせのケイ酸塩化合物を好適に挙げることができる。  As the lipophilic and active ferrosilicate composition which is the supplement of the present invention, the lamellar clay mineral which is a silicate composition selected as a mixed raw material in an artificial synthetic product of heat history silicate is allophane, hysine gel, Pyroferrite, talc, mica, montmorillonite stone group, vermiculite, ryokdeite stone group, kaolinite, or ferrosilicate in combination of two or more types selected from the group of inosilicate can be preferably mentioned. In addition, natural or synthetic silicate compounds such as wollastonite, zonotolite and tobermorite, calcium silicate, magnesium silicate, quartzite, quartz, diatomite, feldspar, zeolite, granite, metamorphic rock, rhyolite, conglomerate, etc. Preferred examples thereof include a single silicate compound selected from the group consisting of rock minerals, aluminosilicate minerals made of mordenite, and water glass and glass alkali silicates.

さらにまた本発明のサプリメントであるケイ酸塩補充組成物としては、シリケートの調製混合原料となるケイ酸塩組成物である、シリケート、含水土質類、熱履歴シリケートもしくは廃ケイ酸塩類の群により選ばれる単独ないし2種以上の組み合わせのケイ酸塩化合物の中からシラノール基を有するケイ酸塩等を目的・用途、さらには作業性等に応じて適宜選び配合することができる。  Furthermore, the silicate supplement composition which is the supplement of the present invention is selected by the group of silicate, hydrous soil, thermal history silicate or waste silicate, which is a silicate composition used as a raw material for preparing and mixing silicate. Silicates having a silanol group or the like can be appropriately selected and blended according to the purpose / use, workability, etc. from singly or in combination of two or more kinds.

特に、本発明においては、改質対象素材に有害物質である油性のダイオキシン類が共存しているとき、この共存しているダイオキシン類に対して、ダイオキシン類に対する分解機能を有するイオン性アルカリを効率よく接触せしめるためにダイオキシン類をエマルジョン化しておく必要があり、この分散エマルジョン化を可能にする乳化剤としてケイ酸塩組成物であり層状粘土鉱物類からなるフェロケイ酸塩組成物は有効である。  In particular, in the present invention, when oil-based dioxins that are harmful substances coexist in the material to be modified, an ionic alkali having a function of decomposing dioxins is efficiently used for the coexisting dioxins. Dioxins need to be emulsified in order to bring them into good contact, and a ferrosilicate composition composed of layered clay minerals is effective as an emulsifier that enables this dispersion emulsion.

シラノール基含有組成物
また、本発明におけるシラノール基含有組成物は、シラノール基を含有するケイ酸塩であればよく、本発明改質処理剤の水和機構を中心とする水和型結晶によるマトリックスの形成を補足して、ポリシロキサン結合からなるシリカポリマーの形成により、ここに形成される形状化活用品の強度を増加させることから好ましい。
Silanol group-containing composition In addition, the silanol group-containing composition in the present invention may be a silicate containing a silanol group, and a matrix of hydrated crystals centering on the hydration mechanism of the modified treatment agent of the present invention. The formation of a silica polymer composed of polysiloxane bonds is preferable because the strength of the shaped and utilized product formed here is increased.

一般にシラノール基含有組成物は、前記した下記組成式(10)

Figure 2006247645
[式中;Mは水素、ナトリウムもしくはカリウム元素]で表されるアルカリシラノール基と水溶出性ナトリウムを保有しているケイ酸アルカリ、もしくはシラノール基保有のケイ酸化合物および活性なナトリウム化合物を構成原料として複合組成物からなる活性な粉粒体であることが好ましい。In general, the silanol group-containing composition has the following composition formula (10):
Figure 2006247645
[In the formula, M is an element of hydrogen, sodium or potassium] An alkali silicate having an alkali silanol group and water-eluting sodium, or a silanol group-containing silicic acid compound and an active sodium compound It is preferable that it is an active granular material made of a composite composition.

さらに、本発明に好適なサプリメントとしては、前述した改質処理剤のナトリウム成分で採択した下記組成式(1)

Figure 2006247645
[式中:Mはナトリウムないしカリウム元素、aは0.1ないし4の数、wは16ないし50の数]で表されるケイ酸アルカリの群より選ばれる単独ないし2種以上の組み合わせのアルカリのケイ酸塩からなる粉粒体をアルカリ補充組成物であると共にケイ酸塩補充組成物として好適に挙げることができる。また、ケイ酸塩アルカリは、耐酸性を求められる活用品を処理調製するときの改質対象素材として有効であり、さらにまた、本発明改質処理剤における水混和体としてのアルカリソルトとしても有効である。Furthermore, as a supplement suitable for the present invention, the following composition formula (1) adopted for the sodium component of the above-described modifying treatment agent is used.
Figure 2006247645
[Wherein, M is an element of sodium or potassium, a is a number of 0.1 to 4, and w is a number of 16 to 50] alone or in combination of two or more selected from the group of alkali silicates A granular material composed of the above silicate is preferably an alkali replenishing composition and a silicate replenishing composition. In addition, silicate alkali is effective as a material to be modified when processing and preparing products that require acid resistance, and is also effective as an alkali salt as a water admixture in the modified treatment agent of the present invention. It is.

インプルーブメント
本発明の改質処理剤を構成する機能付与剤であるインプルーブメントとしては、主として本発明一連の作業工程の作業条件(例えば、混和工程における混和条件の調整、作業可使時間の調整、加工工程における加工性の調整、混和物の硬化・固化体形成速度の調整等)を改善する成分であり、硬化機能を改善するリン酸根組成物、混和物の可使時間を調整するバリウム塩組成物もしくは混和物の分散性を改善する分散媒質組成物の群より選ばれる単独ないし2種以上の組み合わせで構成される粉粒体を好適に挙げることができる。
Improvement As an improvement, which is a function-imparting agent constituting the modifying treatment agent of the present invention, the working conditions of a series of working steps of the present invention (for example, adjustment of mixing conditions in the mixing step, adjustment of working life, Adjustment of processability in processing process, adjustment of curing / solidification rate of admixture, etc.), phosphate radical composition that improves curing function, barium salt composition that adjusts pot life Preferable examples include powders or granules composed of one or a combination of two or more selected from the group of dispersion medium compositions that improve the dispersibility of the product or admixture.

本発明機能付与剤のインプルーブメントであるリン酸根組成物は、本発明の目的・用途・環境に応じて改質処理剤に選択配合することにより、本発明改質処理剤により硬化・固化体等を形成せしめるときに、硬化・固化体等の形成速度を促進する固化促進剤として働き、硬化・固化体等の発現強度等を低下させることなく低アルカリ性の硬化・固化体等を形成せしめることができる。  Phosphate radical composition, which is an improvement of the function-imparting agent of the present invention, is selectively mixed with the modifying agent according to the purpose / use / environment of the present invention, so that it is cured / solidified by the modifying agent of the present invention. It acts as a solidification accelerator that accelerates the formation rate of cured / solidified bodies, etc., and can form low-alkaline cured / solidified bodies and the like without reducing the strength of the cured / solidified bodies. it can.

本発明インプルーブメントであるリン酸根組成物としては、下記組成式(11)

Figure 2006247645
[式中:Gはナトリウム、カリウム、マグネシウム、カルシウム、バリウム、アルミニウム、亜鉛、チタン、ケイ素ならびに鉄の群の単独ないし2種以上の組み合わせの元素、hは1ないし8の数、tはG元素原子価÷2の数、wは零を含む10以下の数]で表される各金属元素のリンのオキシ酸塩化合物の群より選ばれる単独ないし2種以上の組み合わせ化合物からなる粉粒体を好適に挙げることができる。As the phosphate radical composition which is the improvement of the present invention, the following composition formula (11)
Figure 2006247645
[Wherein G is an element of a single or a combination of two or more of the group of sodium, potassium, magnesium, calcium, barium, aluminum, zinc, titanium, silicon and iron, h is a number from 1 to 8, and t is a G element. A powder composed of a single compound or a combination of two or more kinds selected from the group of phosphorus oxyacid salt compounds of each metal element represented by the following formula: valence ÷ 2 number, w is a number of 10 or less including zero] Preferably, it can be mentioned.

また、本発明のインプルーブメントとして好適に採択されるリン酸根組成物は、改質処理剤を構成しているカルシヤ組成物ならびにナトリウム塩化合物当を中和して、形成される製品のpH値を低く調整する役割を果たすことができる。特に、ナトリウムのアルミノケイ酸塩であるゼオライト類が形成された後は、リン酸カルシウム結晶の生成により、カルシウム分が固定化されアルカリ性成分の溶出による環境への二次公害を回避することができる。  Further, the phosphate radical composition suitably adopted as the improvement of the present invention neutralizes the calcium salt composition and the sodium salt compound constituting the modifying treatment agent, and thereby adjusts the pH value of the formed product. Can play a role of low adjustment. In particular, after the formation of zeolites, which are sodium aluminosilicates, the calcium content is fixed by the formation of calcium phosphate crystals, and secondary pollution to the environment due to elution of alkaline components can be avoided.

本発明で好適に採択されるリン酸根組成物具体的な例としては、試薬もしくは工業薬品の中から、リン酸ナトリウム、リン酸カリウム、リン酸マグネシウム、リン酸カルシウム、リン酸バリウム、リン酸アルミニウム、リン酸亜鉛、リン酸チタン、リン酸ケイ素、リン酸鉄、リン酸亜鉛、(抗微生物剤)等の中から適宜選択することができる。  Specific examples of the phosphate radical composition suitably adopted in the present invention include sodium phosphate, potassium phosphate, magnesium phosphate, calcium phosphate, barium phosphate, aluminum phosphate, phosphorus, among reagents or industrial chemicals. It can be appropriately selected from zinc oxide, titanium phosphate, silicon phosphate, iron phosphate, zinc phosphate, (antimicrobial agent) and the like.

さらに、本発明のリン酸根組成物においては、金属製品(自動車、車輌、建材、家電等)の表面処理剤(パーカーライジング処理剤)として汎用されているリン酸系薬品による処理後、産業廃棄物として排出されるリン酸塩を多量に含んだスラッジを有効に利用することができる。また、インプルーブメントとしてのリン酸根組成物として、アルカリ性溶液に除放性を示すリン酸ケイ素からなる粉状体を挙げることができる。  Furthermore, in the phosphate radical composition of the present invention, after treatment with a phosphoric acid chemical widely used as a surface treatment agent (parkerizing treatment agent) for metal products (automobiles, vehicles, building materials, home appliances, etc.), industrial waste As a result, sludge containing a large amount of phosphate discharged as can be used effectively. Moreover, as a phosphate radical composition as an improvement, a powdery body made of silicon phosphate exhibiting release properties in an alkaline solution can be exemplified.

インプルーブメントとして好適なリン酸ケイ素としては、下記組成式(12)

Figure 2006247645
[式中:jは1.0ないし8.0の数]で表されるリン酸ケイ素群より選ばれる「リン酸分の除放性」を有するリン酸ケイ素を挙げることができる。As a silicon phosphate suitable for improvement, the following composition formula (12)
Figure 2006247645
Examples thereof include silicon phosphates having “controlled release properties of phosphoric acid” selected from the group of silicon phosphates represented by [wherein j is a number from 1.0 to 8.0].

リン酸ケイ素における「リン酸分の除放性」は、下記する試験方法により評価することができ、下記式(T−1)

Figure 2006247645
[式中:Xはリン酸ケイ素1gを4規定苛性ソーダ溶液100ml中に攪拌分散せしめ、Xは経過時間(分)、Yは4規定苛性ソーダ溶液中に溶出したリン酸(リンの酸化物)量(mg/100ml)]で表され、リン酸ケイ素のリン酸分(リンの酸化物)溶出の初期溶出量(b)が200以下であり、式中aに相当する平均加水分解速度定数aが0.2以上の範囲にあるリン酸分の溶出状態をいう。The “releasing property of phosphoric acid” in silicon phosphate can be evaluated by the following test method, and the following formula (T-1)
Figure 2006247645
[In the formula: X is 1 g of silicon phosphate stirred and dispersed in 100 ml of 4N caustic soda solution, X is elapsed time (minutes), Y is the amount of phosphoric acid (phosphorus oxide) eluted in 4N caustic soda solution ( mg / 100 ml)], and the initial dissolution amount (b) of the phosphoric acid content (phosphorus oxide) of silicon phosphate is 200 or less, and the average hydrolysis rate constant a corresponding to a in the formula is 0 The elution state of phosphoric acid content in the range of 2 or more.

本発明の機能付与剤であるバリウム塩組成物は、本発明の目的・用途・環境に応じて改質処理剤に選択配合して、本発明の改質処理剤に水系溶媒を介して流動性ないしは可塑性等の混和物としてから活用品とするときの作業工程における施工条件や作業条件、混和物の加工可使時間等、施行作業時の諸条件を改善確保することができる。  The barium salt composition, which is the function-imparting agent of the present invention, is selectively blended with the modifying treatment agent according to the purpose, use, and environment of the present invention, and the fluidity of the modifying treatment agent of the present invention through an aqueous solvent. In addition, it is possible to ensure improvement of various conditions at the time of execution work such as construction conditions and work conditions in the working process when the product is made into a product after being used as an admixture such as plasticity.

本発明機能付与剤であるバリウム塩組成物としては、下記組成式(13)

Figure 2006247645
[式中:fは4以下の数、wは零を含む10以下の数]で表されるアルカリ溶液に可溶なバリウム塩より選ばれる単独ないし2種以上の組み合わせのバリウム塩化合物の粉体が、改質処理剤を活用した均質混和物における作業性を改善調整する上で好ましい。As a barium salt composition which is a function-imparting agent of the present invention, the following composition formula (13)
Figure 2006247645
[In the formula: f is a number of 4 or less, w is a number of 10 or less including zero] Powder of barium salt compound of single or combination of two or more selected from barium salts soluble in alkaline solution However, it is preferable for improving and adjusting workability in a homogeneous mixture utilizing a modifying agent.

本発明のバリウム塩組成物をして採択した粉末状のバリウム塩化合物における作業性等の調整機能は、「バリウムイオンのアルカリ溶液への可溶分=BS」によって推定することができる。「BS」は、下記試験方法により評価することができる。「バリウムイオンのアルカリ溶液への可溶分の試験方法」は、バリウム塩化合物10gを25℃の1規定の苛性ソーダ溶液100ml中に10分間攪拌分散せしめた試料溶液を濾別した採取溶液中のバリウムイオン量をBaOとして測定し、試料バリウム塩化合物中の全バリウム元素をBaOで換算した量を%で表示して、BSのバリウム量を求める。  The adjustment function such as workability in the powdered barium salt compound adopted as the barium salt composition of the present invention can be estimated by “the soluble content of barium ions in an alkaline solution = BS”. “BS” can be evaluated by the following test method. “Method for testing soluble content of barium ions in alkaline solution” refers to barium in a collected solution obtained by filtering a sample solution obtained by stirring and dispersing 10 g of a barium salt compound in 100 ml of a 1N sodium hydroxide solution at 25 ° C. for 10 minutes. The amount of ions is measured as BaO, the amount of all barium elements in the sample barium salt compound converted to BaO is displayed in%, and the barium amount of BS is determined.

本発明の改質処理剤を活用した混和物が、バリウム塩組成物により作業性が調整されて、硬化製品の形成を管理するためには、バリウム塩組成物の「アルカリ溶液への可溶分BS」が、10%以上であることが好適である。「アルカリ溶液への可溶分」が10%以下であるときは、該混和物の施工作業性の管理が困難となり好ましくない。  In order to manage the formation of a cured product in which an admixture utilizing the modifying treatment agent of the present invention is adjusted for workability by the barium salt composition, The “BS” is preferably 10% or more. When the “soluble matter in the alkali solution” is 10% or less, it is not preferable because it becomes difficult to manage the workability of the mixture.

一般に「アルカリ溶液への可溶分」を満足し、安価で入手容易なバリウム塩化合物としては、工業薬品の水酸化バリウムもしくは酸化バリウムが好適である。しかし、形成するゼオライト類に悪影響を与えず、ゼオライト類の形成に充分な作業可使時間を確保できるバリウム塩組成物としてバリウム塩化合物としてケイ酸バリウムは有効である。  In general, barium hydroxide or barium oxide, which is an industrial chemical, is suitable as a barium salt compound that satisfies the “soluble matter in an alkaline solution” and is inexpensive and easily available. However, barium silicate is effective as a barium salt compound as a barium salt composition that does not adversely affect the zeolites to be formed and can ensure a sufficient working life for the formation of zeolites.

バリウム塩組成物としてのケイ酸バリウムは、組成式(8)のfが4以上の数であることが良く、4以上の数ではバリウムイオンの活性を有効に利用することができない。また、組成式(8)のwの数が9以下であることが良く、9以上の数ではバリウム塩化合物の保存安定性が確保されず、本発明の国定を達成することができない。  In the barium silicate as the barium salt composition, f in the composition formula (8) is preferably a number of 4 or more, and if it is a number of 4 or more, the activity of barium ions cannot be used effectively. In addition, the number of w in the composition formula (8) is preferably 9 or less. If the number is 9 or more, the storage stability of the barium salt compound is not ensured, and the national standard of the present invention cannot be achieved.

本発明機能付与剤のインプルーブメントである分散媒質組成物は、本発明の目的・用途・環境に応じて改質処理剤に選択配合して、改質処理剤に対して水を介して改質対象素材と共に混和して目的とする特定形状に成型加工するとき、混和した混和物における混和分散性を改善し、また改質対象素材等に含水している水分の吸着調整剤、流動性ないしは可塑性状態の改善剤として処理作業性を向上せしめるのに好都合である。  The dispersion medium composition, which is an improvement of the function-imparting agent of the present invention, is selectively blended with the modifying treatment agent according to the purpose, application, and environment of the present invention, and the modifying treatment agent is modified through water. When blended with the target material and molded into the desired specific shape, it improves the mixing and dispersibility of the blended mixture, and the moisture adsorption modifier, fluidity or plasticity of the material to be modified, etc. It is convenient to improve the process workability as a condition improver.

本発明機能付与剤のインプルーブメントである分散媒質組成物としては、改質処理剤に相溶性があり、無機質の粉体であり、天然産物で大量に精製生産もしくは廃棄物類として排出されている充填材や粉状体であって、しかも安価に入手容易な材料であることが望ましい。具体的な例として、天然産物では、カオリン、酸性白土、ベントナイト、ボーキサイト、ケイソー土、タルク、ゼオライト、石灰粉、ボーキサイト、パーライト、石膏、貝殻粉末、シリケートならびに火山灰群より適宜選択し、また廃棄物類では、本発明の改質対象素材として選んだ、廃石膏、ガラス屑、高炉スラグ、石炭灰、各種焼却灰、無機質吸着・担持体・媒体類等より適宜選択することができる。  The dispersion medium composition that is an improvement of the function-imparting agent of the present invention is compatible with the modifying agent, is an inorganic powder, and is a natural product and is discharged in large quantities as purified production or wastes. It is desirable that the material is a filler or powder and is easily available at low cost. Specific examples of natural products include kaolin, acid clay, bentonite, bauxite, caustic earth, talc, zeolite, lime powder, bauxite, perlite, gypsum, shell powder, silicate and volcanic ash, and waste Can be appropriately selected from waste gypsum, glass waste, blast furnace slag, coal ash, various incineration ash, inorganic adsorbent / support / medium, etc., selected as the material to be modified in the present invention.

上記の分散媒質組成物は、分散性を求めることから、100μ以下の粉粒体、好むらくは10μ以下の微粉末ないしは微粉末粒子の無機系化合物が有効であり、特に無機系化合物のケイ酸塩系素材は、本発明改質処理剤と相溶性が良く好適な分散媒質組成物として挙げることができる。また、ダイオキシン類等の油分の分散媒質としては、親油性のケイ酸塩系素材が好適であり、層状粘土鉱物であるスメクタイト族の酸性白土やベントナイト、さらに活性白土等を好適に選ぶことができる。  Since the above dispersion medium composition requires dispersibility, it is effective to use an inorganic compound of 100 μm or less, preferably 10 μm or less of fine powder or fine powder particle, and particularly an inorganic compound of silicic acid. The salt-based material can be cited as a suitable dispersion medium composition having good compatibility with the modifying agent of the present invention. Moreover, as the oil dispersion medium such as dioxins, lipophilic silicate materials are suitable, and smectite group acid clay and bentonite, which are layered clay minerals, and activated clay can be preferably selected. .

ファンクションメント
本発明活性化活用成分においては、本発明の目的・用途・環境・作業性等に応じて、本発明結着形状体、特に特定形状、不特定形状、連続形状および集合形状からなる結着形状体に対する補強性、耐熱性、着色性、機能性等の性能向上等が付加されて改良・改質されることが求められる場合がある。この時、本発明の活性化活用成分に多様の機能性を付与する機能付与剤として構成されるファンクションメントを付加・補充することは好ましい。
Functionment In the activation utilization component of the present invention, according to the purpose, application, environment, workability, etc. of the present invention, the binding shape of the present invention, particularly a binding shape comprising a specific shape, an unspecified shape, a continuous shape and a collective shape. In some cases, it is required to be improved and modified by adding performance improvements such as reinforcing properties, heat resistance, coloring properties, and functionality to the shaped body. At this time, it is preferable to add / supplement a functionment configured as a function-imparting agent that imparts various functions to the activation utilization component of the present invention.

したがって、機能付与剤として構成されるファンクショメントは、本発明の改質処理方法で改質処理される結着形状体の物性もしくは機能性を改良・改善する化合物ないしは組成物であり、形成される水不溶性鉱物を成長させる結晶タネ組成物、結着形状体に緩衝性を付与する緩衝帯形成組成物、各種の機能性液状素材を担持する担持吸着組成物、熱に耐える耐熱火組成物、熱遮断性ないしは保温性を発揮する断熱・保温組成物、固−液分離を促進する沈殿凝集組成物もしくは各種の機能性を付与する機能付与組成物の群より選ばれる単独ないし2種以上の組み合わせで構成される粉粒体を好適に挙げることができる。  Therefore, the function constituted as a function-imparting agent is a compound or composition that improves or improves the physical properties or functionality of the bound shape body modified by the modification treatment method of the present invention. A crystal seed composition for growing a water-insoluble mineral, a buffer zone forming composition for imparting buffering properties to a bound shape, a supported adsorption composition for supporting various functional liquid materials, a heat-resistant fire-resistant composition, Single or a combination of two or more selected from the group of a heat insulating and heat insulating composition that exhibits thermal barrier properties or heat retaining properties, a precipitate aggregation composition that promotes solid-liquid separation, or a function-imparting composition that imparts various functionalities The granular material comprised by can be mentioned suitably.

本発明改質処理剤により活性化活用して改質処理される耐水性の結着形状体は、ポリシロキサン結合からなるシリカポリマーに形成と共にアルカリのアルミノケイ酸塩であるゼオライトまたはゼオライト前駆体の形成が重要な役割を果たす。このゼオライトもしくはゼオライト前駆体の結晶成長を促すためのタネとなる結晶タネ組成物を予め改質処理剤に配合しておくこと大変効果的である。  The water-resistant binder shape that is modified by activation utilizing the modification treatment agent of the present invention is formed into a silica polymer composed of a polysiloxane bond, and is also formed into a zeolite or zeolite precursor that is an alkali aluminosilicate. Plays an important role. It is very effective to mix a crystal seed composition as a seed for promoting crystal growth of the zeolite or zeolite precursor in advance in the modifying agent.

ファンクションメントである結晶タネ組成物としては、下記単位格子組成式(14)

Figure 2006247645
[式中:Mは原子価n:の金属陽イオン、X+Yは単位格子当りの四面体数]で表されるアルミノケイ酸の金属塩のゼオライト構造を有するゼオライトの群より選ばれる単独ないし2種以上の組み合わせからなるゼオライトもしくはゼオライト前駆体を好適に挙げることができる。As the crystal seed composition as a functionment, the following unit cell composition formula (14)
Figure 2006247645
[Wherein, M is a metal cation of valence n :, and X + Y is the number of tetrahedrons per unit cell] selected from the group of zeolites having a zeolite structure of a metal salt of aluminosilicate represented by Zeolite or zeolite precursor composed of a combination of

特に本発明における結晶タネ組成物としては、天然品を選ぶこともできるが、水ガラスのほか石炭灰のフライアッシュ、また火山灰を原料として工業生産されている結晶型の定まったゼオライト、例えば4Aタイプの合成ゼオライト等を選ぶこともできる。タネとなるゼオライトは、粒径が10μ以下、好むらくは6μ以下の微細粒子が好ましい。  In particular, as the crystal seed composition in the present invention, a natural product can be selected, but water-glass, coal ash fly ash, or zeolite with a fixed crystal form that is industrially produced using volcanic ash as a raw material, for example, 4A type A synthetic zeolite or the like can also be selected. The seed zeolite is preferably fine particles having a particle size of 10 μm or less, preferably 6 μm or less.

本発明改質処理剤を活用して形状化処理されて形成する耐水性の結着形状体のマトリックスがポリシロキサン結合を中心とするガラス的硬度に強度と共に靭性のある柔軟性が求められるときには、4価のケイ素中心に形成されるポリシロキサン結合に遊びを与える3価のホウ素を組み込ませ、シリカポリマーからなるマトリックスに緩衝帯を形成せしめるホウ素化合物による緩衝帯形成組成物の配合は有効である。  When the matrix of a water-resistant binder-shaped body formed by shaping using the modifying treatment agent of the present invention is required to have a tough flexibility as well as strength in a glassy hardness centered on a polysiloxane bond, It is effective to incorporate a buffer zone-forming composition with a boron compound that incorporates trivalent boron that gives play to a polysiloxane bond formed at a tetravalent silicon center and forms a buffer zone in a matrix made of a silica polymer.

ファンクショメントである緩衝帯形成組成物としては、下記組成式(15)

Figure 2006247645
[式中:Mはリチウム、ナトリウムないしはカリウムのアルカリ金元素、Zはマグネシウム、カルシウムないしは亜鉛のアルカリ土類金属、gは1.0ないしは4.0の数、wは零を含む10以下の数]で表されるアルカリ金属ないしはアルカリ土類金属のホウ素のオキシ酸塩の群の単独ないし2種以上の組み合わせ金属のホウ素のオキシ酸塩化合物からなる緩衝帯形成剤を好適に挙げることができる。As a buffer zone forming composition which is a function, the following composition formula (15)
Figure 2006247645
[Wherein, M is an alkaline gold element of lithium, sodium or potassium, Z is an alkaline earth metal of magnesium, calcium or zinc, g is a number of 1.0 to 4.0, and w is a number of 10 or less including zero. Preferred examples include a buffer zone forming agent composed of a boron oxyacid salt group of an alkali metal or alkaline earth metal boron represented by the following formula:

金属のホウ素のオキシ酸塩化合物としての具体的な例としては、市販試薬もしくは工業薬品の中から、ホウ酸、ホウ酸ナトリム,ホウ酸カリ、ホウ酸カルシウム等を好適に挙げることができる。本発明においては、これらホウ酸塩は、抗生物材(抗菌剤)としても有効であり、本発明改質処理剤の機能付与剤として好ましい。  Specific examples of the metal boron oxyacid salt compound include boric acid, sodium borate, potassium borate, calcium borate and the like from commercially available reagents or industrial chemicals. In the present invention, these borates are effective as an antibiotic material (antibacterial agent) and are preferable as a function-imparting agent for the modified treatment agent of the present invention.

本発明改質処理剤を活用して形成される耐水性の結着形状体において、液状態にある物質の改質対象素材、例えばダイオキシン類や廃油・廃油性成分、さらに例えばイオン性重金属類や塩類を含有している溶液や廃液等、また本発明改質処理剤に有効な機能を示す液状態の機能付与剤等において、本発明改質処理剤で直接対処できないときは、予め機能付与剤である担持吸着体組成物にこれら液状物質を担持・吸着せしめ、粉末状態に改質して本発明に改質・形状化処理工程に付することが好ましい。  In the water-resistant binder formed by utilizing the modification treatment agent of the present invention, a material to be modified of a substance in a liquid state, for example, dioxins, waste oil / waste oil component, further, for example, ionic heavy metals, In the case of a solution or waste solution containing salts, or in a liquid-state function-imparting agent that exhibits an effective function for the present modification treatment agent, when the present modification treatment agent cannot deal directly, a function-imparting agent in advance It is preferable that these liquid substances are supported and adsorbed on the supported adsorbent composition and modified into a powder state and subjected to the reforming and shaping process step of the present invention.

選択するファンクションメントである担持吸着組成物としては、表面積10m/g以上である炭類、活性炭類、非晶質シリカ、珪藻土、活性ケイ酸、活性アルミナならびにゼオライトの群より選ばれる単独ないし2種以上の組み合わせ吸着性担持体からなる吸着性もしくは担持製を有する粉粒体を好適に挙げることができる。The supported adsorbent composition as a functionment to be selected is selected from the group consisting of charcoal, activated carbon, amorphous silica, diatomaceous earth, activated silicic acid, activated alumina and zeolite having a surface area of 10 m 2 / g or more. Preferable examples include adsorbent or supported powder particles composed of a combination adsorbent support of more than one species.

特に、ファンクションメントである担持吸着組成物は、本発明改質処理剤に配合される反応性の高い水酸化ナトリウム等を予め担持吸着体組成物に担持もしくは吸着させて捕捉して、改質処理剤の粉末性を確保して機能性を発揮させるために有効である。さらに、配合される高い反応性の水酸化ナトリウム等を反応系外に遊離したり、放出することなく効果的にゼオライト類の形成に有効に関与させるためにも重要である。  In particular, the supported adsorption composition, which is a functionment, is obtained by supporting or adsorbing highly reactive sodium hydroxide or the like, which is blended in the modification treatment agent of the present invention, on the supported adsorbent composition in advance, and modifying it. It is effective for ensuring the powder properties of the agent and exerting its functionality. Furthermore, it is also important to effectively participate in the formation of zeolites without releasing or releasing the highly reactive sodium hydroxide and the like to be incorporated out of the reaction system.

担持吸着組成物の具体的な一例として、各種の有機化合物や有機質素材を含有している動物・植物類、ならびに農業・畜産・水産の各分野で回収・生産・加工される天然品やその廃棄物、また各種天然品素材の発酵による製品や発酵残渣、紙・パルプ・繊維布類の製造・加工メーカーから排出される廃棄物類、さらにまた、各種プラスチックやその加工現場から排出される有機質素材等を400ないし1000℃で乾留処理して回収される炭を主成分とする炭類、また吸着性能を有するシリカやアルミナを含有している炭−ケイ酸塩の複合品等も好適に挙げることができる。  Specific examples of supported adsorbent compositions include animals and plants that contain various organic compounds and organic materials, as well as natural products that are collected, produced and processed in the fields of agriculture, livestock and fisheries, and their disposal. Products, fermentation products of various natural products, fermentation residues, waste discharged from manufacturers of paper, pulp, and textile fabrics, and processing materials, as well as various plastics and organic materials discharged from the processing site Preferable examples include charcoal mainly composed of charcoal recovered by dry distillation at 400 to 1000 ° C., etc., and charcoal-silicate composite containing silica or alumina having adsorption performance. Can do.

従来型の有機質接着剤等で多孔質性細孔を有する以上の粉粒体類を結着・固結せしめて、利用・取り扱いやすい固結体である顆粒体や成形・構造体としようとするとき、共存している有害物質を無害化処理することもできず、しかも該粉粒体が有している吸着性の多孔質性細孔は潰れてしまい吸着体としての用を成さなくなり、吸着性粉粒体を取り扱いやすい顆粒体や成形・構造体に加工することは困難であった。  By attaching and consolidating the above granular materials having porous pores with conventional organic adhesives, etc., it is intended to form granules and molded / structured bodies that are easy to use and handle Sometimes, the coexisting harmful substances can not be detoxified, and the adsorptive porous pores of the powder are crushed and cannot be used as an adsorbent, It has been difficult to process the adsorbent particles into easy-to-handle granules and molded / structured bodies.

特に本発明の改質対象素材に含水比の高いヘドロや底質等からなる含水泥土を選ぶときは、これら含水泥土に保持されている水分を脱水処理しておくことは、形成される無公害型改質処理剤を固化体で回収するときに好ましく、この脱水処理を兼ねて少なくとも含有する含水比を軽減するために、吸水性の高い担持吸着組成物を予め改質処理剤に配合しておくことは好ましい。  In particular, when selecting a water-containing mud composed of sludge or sediment with a high water content as the material to be modified according to the present invention, dehydrating the water retained in the water-containing mud is a non-polluting process that is formed. It is preferable when recovering the mold reforming treatment agent as a solidified body, and in order to reduce at least the water content ratio that also serves as a dehydration treatment, a supported adsorption composition having high water absorption is blended in the reforming treatment agent in advance. It is preferable to keep it.

本発明改質処理剤が無機質材料により、耐水性で耐熱性の結着形状体からなる資材の形成が可能であること、特に従来技術のセメント類と異なり耐熱性があることから、熱に関連する分野に対応できる資材材料として活用され、本発明改質処理剤は常温での加工・作業性があることから不焼成の耐火物材料や耐火材、さらに不焼成の断熱・保温材等のニーズに応えることができる耐熱火組成物ならびに断熱・保温組成物を添加配合しておくことは好ましい。  Since the modification treatment agent of the present invention can be formed of a water-resistant and heat-resistant binder with an inorganic material, it has heat resistance unlike conventional cements. Because the modified treatment agent of the present invention has processing and workability at room temperature, needs for non-fired refractory materials and refractory materials, as well as non-fired heat insulation and heat insulation materials, etc. It is preferable to add and blend a heat-resistant fire composition capable of meeting the requirements and a heat insulating and heat retaining composition.

ファンクションメントである耐熱火組成物としては、一般に耐火性材料として窯業業界で公知・公用されている材料を好適に挙げることができる。具体的には、少なくとも650℃における熱収縮率が2.0%以下であるマグネシヤ、マグネシヤ−クロム、アルミナ、アルミナ−炭素、マグネシヤ−炭素、炭化ケイ素、窒化ケイ素、シリカ、ケイ酸アルミニウム、ジルコニヤ等を挙げることができる。  As the heat-resistant fire composition that is a functionment, materials generally known and used in the ceramic industry as a fire-resistant material can be preferably cited. Specifically, magnesium, magnesia-chromium, alumina, alumina-carbon, magnesia-carbon, silicon carbide, silicon nitride, silica, aluminum silicate, zirconia, etc. having a heat shrinkage rate of 2.0% or less at least at 650 ° C. Can be mentioned.

また、ファンクションメントである断熱・保温組成物としては、従来アスベスト(石綿)類が使用されてきた保温・断熱材においては、アスベスト類が健康を害する傾向があることから敬遠され、軽くて大量の空気等を包含し、しかも耐熱性がある材料として、ケイ酸カルシウムが求められており、かさ比重が0.05ないし1.2g/ccの範囲にあるかさ密度を有し、少なくとも600℃での熱収縮率が2.0%以下であるケイ酸カルシウムを好適に耐熱火組成物として挙げることができる。  In addition, as insulation and heat insulation compositions that are functionment, asbestos (asbestos) has been used in the heat insulation and insulation materials that have been used in the past. Calcium silicate is required as a heat-resistant material including air and the like, and has a bulk density in the range of 0.05 to 1.2 g / cc and a bulk density of at least 600 ° C. Calcium silicate having a heat shrinkage rate of 2.0% or less can be suitably cited as a heat-resistant fire composition.

本発明の改質処理法によれば、これらの耐熱火組成物ないしは断熱・保温組成物が添加配合された本発明改質処理剤により改質対象素材と共に調製される活性化混和物は、耐火性材料や耐火材、さらに断熱・保温・耐熱材等が求められる分野の原位置・現場等において、予め成型された耐火材や断熱・保温・耐熱材等でなく、原位置・現場等で求められる形状や性状に合わせて原位置・現場等で施工できる所謂付不焼成の耐火材料や断熱・保温・耐熱材料として供給することができて好ましい。  According to the modification treatment method of the present invention, the activated admixture prepared together with the material to be modified by the modification treatment agent of the present invention to which these heat-resistant fire composition or heat insulating and heat retaining composition is added and blended is In-situ or on-site in fields where heat-resistant materials, refractory materials, heat insulation, heat insulation, heat-resistant materials, etc. are required, instead of pre-formed refractory materials, heat insulation, heat insulation, heat-resistant materials, etc. It is preferable because it can be supplied as a so-called non-fired refractory material that can be constructed in-situ or at the site according to the shape and properties to be produced, and as a heat insulating, heat retaining and heat resistant material.

本発明改質処理剤によれば、水分を25ないし100質量%の範囲で含有していて流動性ないし可塑性の含水土質・汚泥ないしは底質である一般素材類ないしは有害素材類からなる改質対象素材を処理対象物にして、再利用可能な再資源化資材の処理調製することが可能であることから、特に底質を形成している湖沼・ダム等に水分散している含水土質・汚泥・藻類・アオコ、リン成分ないしは窒素成分の群より選ばれる単独ないし2種以上の組み合わせ成分等からなる成分類を予め沈殿凝縮せしめて脱水処理された底質として再資源化処理することは、環境浄化の立場から好ましい。  According to the modification treatment agent of the present invention, the modification target is composed of general materials or harmful materials which contain water in a range of 25 to 100% by mass and are fluid or plastic hydrous soil / sludge or sediment. Since it is possible to prepare recyclable materials that can be reused as materials to be treated, hydrous soil and sludge dispersed in lakes, dams, etc. that form sediments in particular.・ It is environmentally friendly to pre-precipitate and condense components consisting of algae, aoko, phosphorus component or nitrogen component, or a combination of two or more types of components into sediments that have been precipitated and condensed in advance. It is preferable from the viewpoint of purification.

ファンクションメントである沈殿凝集組成物としては、カルシヤを少なくとも20質量%以上含有するカルシウム塩組成物、廃棄物類組成物、カルシヤ含有鉱物組成物および炭カル変性組成物の群より選ばれる単独ないし2種以上の組み合わせのカルシウム塩化合物を主成分とする組成物であり、粒径が1000μ以下であり、水溶出pH値が13未満であり、水に浮遊分散もしくは溶解している含水土質、汚泥、藻類、アオコ、リン成分ないしは窒素成分の群より選ばれる単独ないし2種以上の組み合わせ成分に接触せしめて凝集沈殿せしめるカルシヤ含有組成物からなる沈殿凝集組成物を好適に挙げることができる。  As the precipitation agglomeration composition as a functionment, one or two selected from the group consisting of a calcium salt composition containing at least 20% by mass of calcium, a waste composition, a calcium-containing mineral composition, and a charcoal cal-modified composition. Hydrous soil, sludge having a particle size of 1000 μm or less, a water elution pH value of less than 13, and suspended or dispersed in water. Preferable examples include a precipitated aggregate composition composed of a calcium-containing composition that is brought into contact with one or two or more combined components selected from the group of algae, blue seaweed, phosphorus component, or nitrogen component to cause aggregation.

本発明改質処理剤を活用して処理調製される結着形状体には、それぞれの目的・用途に応じて多様性が期待できる基礎があることから、それぞれ異なった機能性を本発明処理剤に付加して、それぞれの多機能性を発揮させることができる。このとき本発明処理剤に添加配合される各種の機能付与組成物を本発明改質処理剤に予め配合してワンパック化しておくこと作業性との簡素化から好ましい。  Since the binder-shaped body processed and prepared by utilizing the modified treatment agent of the present invention has a basis on which diversity can be expected according to each purpose and application, the different treatment properties of the present invention treatment agent are provided. In addition to the above, each multifunction can be exhibited. At this time, it is preferable in view of simplification of workability that various function-imparting compositions added and blended with the treatment agent of the present invention are pre-blended with the modification treatment agent of the present invention to form a one-pack.

ファンクションメントである機能付与組成物としては、顔料、着色剤、活性剤、充填剤、磁石と磁性体、触媒、酸化性化合物、凝集分離剤、農薬・除草剤・肥料・微生物栄養剤、植物種子や菌類、抗微生物剤、撥水剤および機能付加剤等の群より選ばれる単独ないし2種以上の組み合わせの化合物や組成物からなり、粒径が50μ未満の粉末体もしくは粉粒体が好ましい。具体的な形状としては、粉状、砂状、塊状、針状、柱状、球状、中空状、板状、フレーク状、変形状もしくは各種の形状物を選ぶことができる。  Function-providing compositions that are functionments include pigments, colorants, activators, fillers, magnets and magnetic materials, catalysts, oxidizing compounds, aggregating and separating agents, pesticides, herbicides, fertilizers, microbial nutrients, plant seeds And a powder or granular material having a particle size of less than 50 μm, which is composed of a single compound or a combination of two or more selected from the group of fungi, fungi, antimicrobial agents, water repellents and functional additives. As specific shapes, powder, sand, lump, needle, column, sphere, hollow, plate, flake, deformed or various shapes can be selected.

本発明における機能付与組成物は、当業界で公知・公用の材料や素材類、工業薬品、農業用肥料・農薬ならびに試薬品、特注品等であり、またプラスチック加工、セメント加工、木材加工等で使用する塗料、接着剤、各種の改質処理剤等から適宜選んで採択することができる。しかし、本発明改質処理剤に採択される機能付与組成物は、ここに記載される材料、素材類、化合物ないしは組成物類に限定されるものでない。  The function-imparting composition in the present invention is a publicly known or publicly used material or materials in the industry, industrial chemicals, agricultural fertilizers / agrochemicals, reagent products, custom-made products, etc., and plastic processing, cement processing, wood processing, etc. It can be selected as appropriate from the paints, adhesives, and various modifying treatment agents to be used. However, the function-imparting composition adopted for the modification treatment agent of the present invention is not limited to the materials, raw materials, compounds, or compositions described herein.

顔料としては、当業界で公知・公用の各種体質顔料はすべて採択することができ、カーボンブラック、酸化チタン、シリカ系微粉末(ホワイトカーボン等)、溶融シリカ、ケイ酸塩や粘土類、アルミナ、溶融アルミナ、貝殻等炭酸カルシウム、炭酸マグネシウム、酸化ジルコニウム等を好適に挙げることができる。さらに、酸化鉄(弁柄等)、水酸化鉄、塩化鉄、酸化クロム、クロム酸鉛、(黄鉛等)、群青、酸化亜鉛やホウ酸亜鉛、各種金属の酸化物の焼成顔料、無機質有色顔料、非酸化物、金属・合金類等、さらに有機質顔料(不溶性アゾ顔料、縮合多環型顔料、キナクリドン系顔料、イソインドリノン系顔料、シアンニンブルー、シアンニングリーン等)であるアルカリ性に強い顔料粉体を好適に挙げることができる。  As the pigment, all known and publicly used extender pigments in the industry can be adopted, such as carbon black, titanium oxide, silica fine powder (white carbon, etc.), fused silica, silicates and clays, alumina, Preferable examples include calcium carbonate such as fused alumina and shells, magnesium carbonate, and zirconium oxide. In addition, iron oxide (valve, etc.), iron hydroxide, iron chloride, chromium oxide, lead chromate (yellow lead, etc.), ultramarine, zinc oxide and zinc borate, calcined pigments of various metal oxides, inorganic colors Resistant to alkalinity of pigments, non-oxides, metals and alloys, and organic pigments (insoluble azo pigments, condensed polycyclic pigments, quinacridone pigments, isoindolinone pigments, cyanine blue, cyanine green, etc.) Preferred examples include pigment powder.

着色剤としては、上記の無機・有機顔料に加えて、当業界で公知・公用されている各種有機質着色化合物、各種インキならびに天然・合成の染料等を単独ないし2種以上の組み合わせの着色剤より選ぶことにより、希望色相を製品に付与することが可能となる。  As the colorant, in addition to the above-mentioned inorganic / organic pigments, various organic coloring compounds, various inks and natural / synthetic dyes that are known and used in the industry are used alone or in combination of two or more kinds. By selecting, it becomes possible to give a desired hue to the product.

活性剤としては、リン酸アルミ、ホウ酸、各種の触媒、光触媒の酸化チタン、廃リン酸スラッジ等を好適に挙げることができる。また機能付与組成物の磁性体としては、一般的な酸化鉄を磁器化したフェライト、酸化鉄、酸化クロム、コバルト等の粉状体を上げることができる。特殊な磁性体として、鉄−ホウ素、コバルト−ホウ素、ネオヂウム−鉄、ネオヂウム−ホウ素等の複合金属による磁性体の粉状体を挙げることができる。  Preferred examples of the activator include aluminum phosphate, boric acid, various catalysts, photocatalyst titanium oxide, and waste phosphate sludge. Moreover, as a magnetic body of a function-providing composition, powdery bodies such as ferrite, iron oxide, chromium oxide, and cobalt, which are generalized iron oxides, can be raised. Examples of the special magnetic material include a powdered magnetic material made of a composite metal such as iron-boron, cobalt-boron, neodymium-iron, or neodymium-boron.

充填剤としては、ダイヤモンド、ガラス、窒化物、炭化物、セラミック、陶磁器、酸化ケイ素(珪石、珪砂、シリカヒュム、溶融シリカ等)、岩石(蛇紋岩、安山岩、蛭石等)、粘土(カオリン、ベントナイト、ガイロメ、タルク、マイカ、木状粘土等)、焼成クレー(カオリン、粘土等)、石こう、リン鉱石、鉄鉱石、マンガン鉱、貝殻、ジルコンサンド等であって小塊状、フレーク状、繊維状、粉末状充填剤を挙げることができる。  Fillers include diamonds, glass, nitrides, carbides, ceramics, ceramics, silicon oxides (silica, silica sand, silica hum, fused silica, etc.), rocks (serpentine, andesite, meteorite, etc.), clay (kaolin, bentonite, Gyrome, talc, mica, woody clay, etc.), calcined clay (kaolin, clay, etc.), gypsum, phosphorus ore, iron ore, manganese ore, shells, zircon sand, etc. in small blocks, flakes, fibers, powders Can be mentioned.

磁石と磁性体としては、硬質磁性材料である希土類焼結磁石、フェライト焼結磁石、ボンド磁石、鋳造磁石、また半硬質ないしは軟質磁性材料である焼結ケイ素鋼、PB系やPC系焼結体、さらにハードないしはソフトのフェライトである酸化物軟質磁性材料や磁性ステンレス等であり、鉄、ニッケル、コバルト等の金属ならびに合成された複合合金類等から、さらにまたそれぞれの加工されている永久磁石である希土類磁石、塑性加工磁石、フェライト磁石、圧延磁石、ボンド磁石、鋳造磁石、または軟質磁石である金属系軟質磁性材料、酸化物系軟質磁性材料、焼結軟質磁性材料、アモルファス系軟質磁性材料、ナノ結晶軟質磁性材料等から選ぶことをできる。  Magnets and magnetic materials include rare earth sintered magnets that are hard magnetic materials, ferrite sintered magnets, bonded magnets, cast magnets, sintered silicon steels that are semi-rigid or soft magnetic materials, PB-based and PC-based sintered materials In addition, it is a soft magnetic material such as hard or soft ferrite, magnetic stainless steel, etc., from metals such as iron, nickel, cobalt, etc. and synthesized composite alloys, etc., and each processed permanent magnet. Some rare earth magnets, plastic working magnets, ferrite magnets, rolled magnets, bonded magnets, cast magnets, or soft, metallic soft magnetic materials, oxide soft magnetic materials, sintered soft magnetic materials, amorphous soft magnetic materials, You can choose from nanocrystalline soft magnetic materials.

触媒としては、白金、パラジウム、ニッケル、亜鉛、鉄、銀、銅等の金属ないしは合金、ならびにクロム、鉄、亜鉛、モリブデン、セレン、セシウム、銅等の単独ないしは組み合わせの金属酸化物もしくは塩類・複合塩類等、さらにゼオライト、アルミノケイ酸塩、各種の鉱物等を挙げることができる。  Catalysts include platinum, palladium, nickel, zinc, iron, silver, copper, and other metals or alloys, and chromium, iron, zinc, molybdenum, selenium, cesium, copper, etc. Salts, etc., and zeolites, aluminosilicates and various minerals can be mentioned.

酸化性化合物として、塩素酸カリウム、塩素酸ナトリウム、塩素酸アンモニウム、塩素酸パリウム、塩素酸カルシウム等の塩素酸塩類;過塩素酸カリウム、過塩素酸ナトリウム、過塩素酸アンモニウム等の過塩素酸塩類;過酸化カリウム、過酸化ナトリウム、過酸化カルシウム、過酸化マグネシウム、過酸化バリウム等の無機過酸化物類、亜塩素酸カリウム、亜塩素酸ナトリウム、亜塩素酸銅等の亜塩素酸塩類;臭素酸カリウム、臭素酸ナトリウム、臭素酸マグネシウム等の臭素酸塩類;硝酸アンモニウム、硝酸ナトリウム、硝酸カリウム、硝酸パリウム、硝酸銀等の硝酸塩類を好適に挙げることができる。  As oxidizing compounds, chlorates such as potassium chlorate, sodium chlorate, ammonium chlorate, parium chlorate, calcium chlorate; perchlorates such as potassium perchlorate, sodium perchlorate, ammonium perchlorate ; Inorganic peroxides such as potassium peroxide, sodium peroxide, calcium peroxide, magnesium peroxide and barium peroxide; chlorites such as potassium chlorite, sodium chlorite and copper chlorite; bromine; Preferable examples include bromates such as potassium acid, sodium bromate, and magnesium bromate; and nitrates such as ammonium nitrate, sodium nitrate, potassium nitrate, parium nitrate, and silver nitrate.

さらに、よう素酸カリウム、よう素酸ナトリウム、よう素酸カルシウム等のよう素酸塩類;過マンガン酸カリウム、過マンガン酸アンモニウム等の過マンガン酸塩類;重クロム酸ナトリウム、重クロム酸アンモニウム等の重クロム酸塩類;過よう素酸ナトリウム、メタ過よう素酸、二酸化クロム、二酸化鉛、亜硝酸ナトリウム、次亜塩素酸カリウム、次亜塩素酸ナトリウム、ペルオキソニ硫酸カリウム、ペルオキソニ硫酸ナトリウム、ペルオキソニ硫酸アンモニウム、ペルオキソほう酸カリウム、ペルオキソほう酸アンモニウム等を好適に挙げることができる。  Further, iodates such as potassium iodate, sodium iodate, calcium iodate; permanganates such as potassium permanganate, ammonium permanganate; sodium dichromate, ammonium dichromate, etc. Dichromates; sodium periodate, metaperiodate, chromium dioxide, lead dioxide, sodium nitrite, potassium hypochlorite, sodium hypochlorite, potassium peroxodisulfate, sodium peroxodisulfate, ammonium peroxodisulfate, Preferable examples include potassium peroxoborate and ammonium peroxoborate.

凝集分離剤としては、水域分散粒子、藻類(アオコ等)や含水粒子類を沈降凝集させる材料凝集沈殿剤や藻類のでもある無機系では硫酸アルミに無(硫酸バンド)塩化第二鉄、ポリ塩化アルミニウム(PAC)等があり、有機系ではアクリル系もしくはポリエステル系の有機合成高分子化合物等を好適に挙げることができる。  As an aggregating / separating agent, water-dispersed particles, materials that agglomerate algae (blue water, etc.) and hydrous particles, and agglomerate-precipitating agents and algae are also inorganic systems that do not contain aluminum sulfate (sulfate band) ferric chloride, polychlorinated There are aluminum (PAC) and the like, and an organic synthetic polymer compound such as acrylic or polyester is preferable.

農薬・除草剤・肥料・微生物栄養剤としては、農業・園芸等の分野で一般に汎用・採択されている農薬・除草剤・肥料・微生物栄養剤等を挙げることができる。特に土壌地盤、農地や地盤改良区域等における無害化処理に採択するときは、農地や地盤改良区域等土壌の改質と同時に、施肥・除草・殺虫等の効果を同時に付与する上からも農薬・肥料・微生物活性栄養剤等を本発明改質処理剤に付加・補足することは好ましい。  Examples of the agrochemicals, herbicides, fertilizers, and microbial nutrients include agricultural chemicals, herbicides, fertilizers, and microbial nutrients that are generally used and adopted in fields such as agriculture and horticulture. In particular, when adopting detoxification treatment in soil ground, farmland or ground improvement areas, etc., it is also possible to improve the soil such as farmland and ground improvement areas, and at the same time provide the effects of fertilization, weeding, insecticide, etc. It is preferable to add and supplement fertilizers, microbial active nutrients, and the like to the modified treatment agent of the present invention.

植物の種や菌類としては、本発明改質処理剤を土壌地盤等、特に農地や地盤改良区域等における無害化処理に採択するときは、農地や地盤改良区域等土壌の改質と同時に、植物類の育成・繁茂の効果を同時に付与するために、土地の環境や用途目的に応じた植物の種や菌類を予め本発明改質処理剤に添加配合しておくことは好ましい。  As plant seeds and fungi, when adopting the treatment agent of the present invention for detoxification treatment in soil ground, especially in farmland and ground improvement areas, etc. In order to simultaneously impart the effects of breeding and overgrowth, it is preferable to previously add and blend plant seeds and fungi according to the land environment and purpose of use in the present modification treatment agent.

抗微生物剤としては、下記組成式(16)

Figure 2006247645
[式中:Dは1価または2かの銀、銅、亜鉛もしくはニッケル元素、Tはカルシウム、マグネシウム、ホウ素、アルミニウム、炭素、ケイ素、リンもしくは硫黄元素、Vは零を含む3.5以下の数、wは零を含む24.0以下の数、yは0.5ないし1.0の数、xは0.5ないし3.0の数]で表される銀、銅、亜鉛、ニッケル元素の塩でカルシウム、マグネシウム、ホウ素、アルミニウム、炭素、ケイ素、リン、硫黄元素のオキシ酸塩化合物の群の単独ないし2種以上の組み合わせ抗微生物剤を好適に挙げることができる。As an antimicrobial agent, the following composition formula (16)
Figure 2006247645
[Wherein D is a monovalent or bivalent element of silver, copper, zinc or nickel, T is an element of calcium, magnesium, boron, aluminum, carbon, silicon, phosphorus or sulfur, and V is 3.5 or less including zero. Number, w is a number of 24.0 or less including zero, y is a number of 0.5 to 1.0, x is a number of 0.5 to 3.0], silver, copper, zinc, nickel element Preferred examples of the salt include a single group or a combination of two or more types of oxyacid salt compounds of calcium, magnesium, boron, aluminum, carbon, silicon, phosphorus, and sulfur elements.

撥水剤としては、前述した吸着性担持体に撥水性を有するシラン化合物、オルガノシロキサン類、オルガノポリシロキサン類等、さらにフッ素系化合物等の液状撥水剤を無機質吸着担持体に予め担持させた撥水性を有する粉状体を好適に採択することができる。オルガノシロキサン類としては、いわゆるシランカップリング剤で有機樹脂と反応可能なX基(アミノ基、エポキシ貴、メタクリロシキ基)と無機材料と融合可能なシラノール基を有するシラン化合物、シラン化合物の変性もしくはポリマー化せしめたオルガノポリシロキサン類等を好適に挙げることができる。  As the water repellent, a liquid water repellent such as a silane compound, organosiloxane, organopolysiloxane, etc. having water repellency, and a fluorine-based compound was previously supported on the inorganic adsorbent support. A powdery body having water repellency can be suitably adopted. Organosiloxanes include silane compounds having X groups (amino groups, epoxy nobles, methacryloxy groups) that can react with organic resins with so-called silane coupling agents and silanol groups that can be fused with inorganic materials, modified silane compounds or polymers Suitable organopolysiloxanes can be mentioned.

機能性付加剤としては、従来公知・公用されてきた各種の機能付与剤を挙げることができる。具体的には、緩衝帯形成剤、防錆剤、発泡剤、消泡剤、重金属類不溶化材、重金属類固定化材、抗酸化防止剤、滑り止め剤、吸水剤、結露防止剤、融雪剤、凍結融解剤、凝集剤、沈殿剤、水処理剤、アブロッキング剤、保存剤、膨張剤、吸着剤、不燃・難燃剤、発色剤、発煙剤、発泡剤等を挙げることができる。  Examples of the functional additive include various conventionally known and publicly used function-imparting agents. Specifically, buffer zone forming agent, rust preventive agent, foaming agent, antifoaming agent, heavy metal insolubilizing material, heavy metal immobilizing material, antioxidant, anti-slip agent, water absorbing agent, anti-condensation agent, snow melting agent , Freezing and thawing agent, flocculant, precipitant, water treatment agent, blocking agent, preservative, swelling agent, adsorbent, incombustible / flame retardant, color former, fuming agent, foaming agent and the like.

さらに、紫外線・近赤外・赤外線吸収剤、赤外・遠赤外線発生剤、放射線発生剤、発光体、光触剤、酸化剤、還元剤、火薬、起爆剤、弾性体、熱伝導体、導電体、強磁性体、常磁性体、反磁性体、誘電体、帯電防止剤、電磁波吸収・遮蔽剤、絶縁材、防臭剤、消臭剤、芳香剤、香料、界面活性剤、忌避剤、殺虫剤、防虫剤、除草剤、抗微生物剤、抗菌剤、防腐剤、植物種、各種活性剤等を上げることができる。  Furthermore, ultraviolet / near infrared / infrared absorbers, infrared / far infrared generators, radiation generators, illuminants, photocatalysts, oxidizing agents, reducing agents, explosives, detonators, elastic bodies, thermal conductors, conductive materials Body, ferromagnetic material, paramagnetic material, diamagnetic material, dielectric, antistatic agent, electromagnetic wave absorption / shielding agent, insulating material, deodorant, deodorant, fragrance, fragrance, surfactant, repellent, insecticide Agents, insect repellents, herbicides, antimicrobial agents, antibacterial agents, preservatives, plant species, various active agents, and the like.

本発明改質処理剤に付加・補足される機能付与剤は、前述した硫酸根含有組成物ないしは硫化物含有組成物であるサルファメント;アルカリ補充組成物、鉄塩補充組成物もしくはケイ酸塩補充組成物であるサプリメント;リン酸根組成物、バリウム塩組成物もしくは分散媒質組成物であるインプルーブメント;さらに繊維質組成物、骨材質組成物、結晶タネ組成物、緩衝帯形成組成物、担持吸着組成物、耐熱火組成物、断熱・保温組成物、沈殿凝集組成物もしくは機能付与組成物の群より選ばれる単独ないし2種以上の組み合わせで構成されている複合型の機能付与剤の中からそれぞれの目的・用途、さらには作業性等に応じて適宜選ぶことができる。  The function-imparting agent added to or supplemented to the modified treatment agent of the present invention is a sulfate that is a sulfate group-containing composition or a sulfide-containing composition as described above; an alkali supplement composition, an iron salt supplement composition, or a silicate supplement. Supplements as compositions; Improvements as phosphate radical compositions, barium salt compositions or dispersion medium compositions; and fiber compositions, bone material compositions, crystal seed compositions, buffer zone forming compositions, supported adsorption compositions Each of the composite-type function-imparting agents composed of a single or a combination of two or more selected from the group of products, heat-resistant fire composition, heat insulation / heat insulation composition, precipitation aggregation composition or function-imparting composition It can be appropriately selected according to the purpose / use, and workability.

レインホースメント
本発明の結着形状体においては、その結着形状体の求められる分野ならびに目的・用途に応じて、既存のセメント二次製品に匹敵する強度物性が求められるときがある。このような場合、セメント二次製品における場合と同様に各種の補強材を補足成分としての補強成分として加えて強度等の補強された結着形状体を調製する必要がある。したがって、本発明活性化活用成分に多様の機能性を付与する機能付与剤として構成される補強性効果を発揮できるレインホースメントとして、結着形状体を補強・補足する繊維質組成物、同様に細骨材ないしは粗骨材の群より選ばれる単独ないし2種以上の組み合わせの補強性材料を付加・補充することができる。
Rain reinforcement In the bound shape body of the present invention, strength properties comparable to existing secondary cement products may be required depending on the field in which the bound shape body is required and the purpose and application. In such a case, as in the case of the cement secondary product, it is necessary to add various reinforcing materials as reinforcing components as supplemental components to prepare a bound shaped body reinforced with strength and the like. Accordingly, as a rain reinforcement capable of exerting a reinforcing effect configured as a function-imparting agent that imparts various functions to the activation utilization component of the present invention, a fibrous composition that reinforces and supplements the bound shape, similarly A single or a combination of two or more reinforcing materials selected from the group of fine aggregates or coarse aggregates can be added and supplemented.

本発明レインホースメントである骨材としては、コンクリート製品等で使用されている粒径5mmφ以下の砂・砕石等からなる「細骨材」ならびに粒径5mmφ以上の砂利・砕石等からなる「粗骨材」もしくはこれらが混合されている「混合骨材」を好適に採択することができる。また、嵩比重が0.2ないし3.5g/ccの範囲にある結晶状、砂状、塊状、砕石、カレット重量・普通・軽量骨材、粒状、針状、柱状、球状、中空状、板状、棒状、フレーク状、不特定形状等の各種形状の無機質や有機質の天然材料や合成加工材料等を粗骨材として選ぶこともできる。  As the aggregate which is the rain reinforcement of the present invention, “fine aggregate” made of sand, crushed stone or the like having a particle diameter of 5 mmφ or less, and “crude” made of gravel or crushed stone having a particle diameter of 5 mmφ or more, which are used in concrete products, etc. “Aggregates” or “mixed aggregates” in which these are mixed can be suitably employed. Also, crystalline, sandy, lump, crushed stone, cullet weight / ordinary / lightweight aggregate, granular, needle-like, columnar, spherical, hollow, plate with bulk specific gravity in the range of 0.2 to 3.5 g / cc Inorganic, organic natural materials, synthetic processed materials, and the like having various shapes such as shapes, rods, flakes, and unspecified shapes can be selected as the coarse aggregate.

また、本発明レインホースメントである粗骨材として、粒径が5mmφ以上で嵩比重が0.9g/cc未満の天然もしくは合成の軽量骨材(バーミュキュライト、パーライト、人工材等)も選ぶことができる。さらにまた、嵩比重が2.5g/cc以上の重たい骨材[鉄鋼石やマンガン鉱等]を、また日常生活や産業界から廃出される無機質素材を主成分とする廃棄物類(廃ガラスのカレット、セメント製品廃物、窯業製品、ガラクタ屑、リサイクル品、建設廃土、焼却灰類の溶融スラッグ等)の各種形状に選別により形状化処理されている廃棄物加工品も、また本発明の改質対象素材である砂粒状の骨材類も本発明の目的・用途に応じて本発明粗骨材として好適に採択することができる。  Further, as the coarse aggregate which is the rain reinforcement of the present invention, natural or synthetic lightweight aggregates (vermiculite, perlite, artificial materials, etc.) having a particle size of 5 mmφ or more and a bulk specific gravity of less than 0.9 g / cc are also available. You can choose. In addition, heavy aggregates [steel stone, manganese ore, etc.] with a bulk specific gravity of 2.5 g / cc or more, and wastes mainly composed of inorganic materials that are discarded from daily life and industry (waste glass Processed waste products that have been shaped into various shapes such as cullet, cement product waste, ceramic products, junk waste, recycled products, construction waste soil, incinerated ash molten slugs) are also modified by the present invention. Sand granular aggregates, which are quality target materials, can also be suitably adopted as the coarse aggregate of the present invention according to the purpose and application of the present invention.

本発明レインホースメントである細骨材としては、粒径が5mm以下であり、かさ密度が0.2ないし3.5g/ccの範囲にある結晶状、砂状、塊状、粒状、針状、柱状、球状、中空状、板状、棒状、フレーク状、不特定形状等の各種形状無機質や有機質天然材料や合成加工材料、無機質粉粒体、カレット類、砂、小砂利ならびに重量・軽量骨材の群より選ばれえる単独ないし2種以上の組み合わせ粉状体・砂粒体・繊維体・特定形状体を好適に選ぶことができる。具体的には、一般の砂類のほかに、嵩比重が、0.9g/cc未満の天然もしくは合成の軽量骨材(バーミュキュライト、パーライト、人工材等)を好適に挙げることができる。  As the fine aggregate which is the rain reinforcement of the present invention, the particle size is 5 mm or less, the bulk density is in the range of 0.2 to 3.5 g / cc, crystalline, sandy, massive, granular, needle-like, Various shapes such as columnar, spherical, hollow, plate-like, rod-like, flake-like, unspecified shape, inorganic and organic natural materials and synthetic processed materials, inorganic powders, cullet, sand, small gravel, and weight / lightweight aggregate A single powder or a combination of two or more powders, sand particles, fibers and specific shapes that can be selected from these groups can be suitably selected. Specifically, in addition to general sands, natural or synthetic lightweight aggregates (vermiculite, pearlite, artificial materials, etc.) having a bulk specific gravity of less than 0.9 g / cc can be preferably mentioned. .

さらに嵩比重が2.5g/cc以上の重たい骨材[鉄鋼石やマンガン鉱等]を、また日常生活や産業界から廃出される無機質素材を主成分とする廃棄物類(廃ガラスのカレット、セメント製品廃物、窯業製品、ガラクタ屑、リサイクル品、建設廃土、焼却灰類の溶融スラッグ等)の各種形状に選別形状化処理されている廃棄物加工品も本発明の改質対象素材の砂粒状の骨材類として好適に採択することができる。  In addition, heavy aggregates [steel stone, manganese ore, etc.] with a bulk specific gravity of 2.5 g / cc or more, and wastes composed mainly of inorganic materials that are discarded from daily life and industry (waste glass cullet, Cement product waste, ceramic products, junk waste, recycled products, construction waste soil, incinerated ash molten slug, etc. It can be suitably adopted as granular aggregates.

本発明改質処理剤を活用して形状化処理された耐水性の結着形状体に強度と共にフレキシビリィテーを求められる時は、繊維質素材等を混入することは効果的である。その見地から、本発明改質処理剤に予め繊維質素材である繊維質組成物を補強成分として配合してワンパックにしておくことは好ましい。本発明補強成分である繊維質組成物は、長い方で5mm未満であり、金属繊維、ガラス繊維、ロックウール、炭素繊維、鉱物繊維、植物性繊維ならびに有機質繊維の群より選ばれる単独ないし2種以上の組み合わせの繊維状の粉粒体を好適に挙げることができる。  It is effective to mix a fibrous material or the like when flexibility and flexibility are required for a water-resistant binder shaped body that has been shaped using the modification treatment agent of the present invention. From this point of view, it is preferable that a fiber composition, which is a fibrous material, is blended in advance as a reinforcing component into the modification treatment agent of the present invention to form a one-pack. The fiber composition which is the reinforcing component of the present invention is less than 5 mm in the longer side and is selected from the group consisting of metal fiber, glass fiber, rock wool, carbon fiber, mineral fiber, vegetable fiber and organic fiber. The fibrous powder of the above combination can be preferably exemplified.

本発明補強成分である繊維質組成物としては、既にプラッスチックスの加工業界等で採用されている長い方で5mm未満である金属粉(ステンレス、ケイ素、亜鉛、アルミニウム、ニッケルおよび鉄等の合金を含む金属系の粉末)、金属繊維、ガラス繊維、ロックウール、炭素繊維、鉱物繊維、無機質繊維、ウイスパー、植物性繊維、有機質繊維からなる繊維質物質類を好適に挙げることができる。  As the fibrous composition which is a reinforcing component of the present invention, a metal powder (stainless steel, silicon, zinc, aluminum, nickel, iron, etc.) which is already used in the plastics processing industry etc. and which is less than 5 mm is used. Preferred examples include fibrous materials comprising metal powder, metal fiber, glass fiber, rock wool, carbon fiber, mineral fiber, inorganic fiber, whisper, vegetable fiber, and organic fiber.

本発明の改質処理剤においては、予め乾燥物基準で改質処理剤である活性化活用成分100質量部に対して、それぞれ選ばれた機能付与剤の単独ないし複数からなる機能付与剤を400質量部以下の量で付加されて、本発明の混和工程において、必要な活性化活用成分および機能付与剤を個別配合することもできるが、予め均質混合されているワンパック品として取り扱うこともできる。これらの改質処理剤の形態は、本発明の目的・用途・環境・作業性等に応じて、適宜の方法・手段で採択することができるが、予め行う予備実験により、物性・性状ならびに方法・手段等を確認することが好ましい。  In the modifying agent of the present invention, 400 function-imparting agents each consisting of one or a plurality of each of the function-imparting agents selected in advance with respect to 100 parts by mass of the activation utilization component that is the modifying agent on a dry matter basis. In addition, the necessary activation utilization component and the function-imparting agent can be individually added in the mixing step of the present invention, but can also be handled as a one-pack product that has been homogeneously mixed in advance. . The form of these modifying treatment agents can be adopted by an appropriate method / means depending on the purpose, application, environment, workability, etc. of the present invention. -It is preferable to confirm the means.

[結着形状体]
本発明技術によれば、水系環境に溶出する有害な元素群およびダイオキシン類からなる有害物質を共存するケイ酸塩系化合物を主成分とする熱履歴シリケートの粉粒体または含水体である改質対象素材に水系溶媒を介してpH値で12を超える活性化機能を有する改質処理剤、さらに必要に応じて機能付与剤を加えて混和する一連の作業工程に付する改質処理方法を採択して、改質対象素材に共存する有害物質が固定・不溶化され、ダイオキシン類は分解された無害化処理が施され、また改質対象素材の粉粒体がpH値10未満で確保されて水中での再泥化の阻止された形状化処理が施されて無公害型再資源化資材として提供される耐水性の結着形状体を調製することができる。
[Binder shape]
According to the technology of the present invention, a heat history silicate granular material or hydrated body mainly composed of a silicate compound coexisting a harmful element group eluting in an aqueous environment and a harmful substance composed of dioxins Adopted a modification treatment method that includes a modification processing agent having an activation function exceeding 12 in pH value through an aqueous solvent and a series of work steps in which a function-imparting agent is added and mixed as necessary. Then, harmful substances coexisting in the material to be modified are fixed and insolubilized, the dioxins are decomposed and detoxified, and the granular material of the material to be modified is secured at a pH value of less than 10 to Thus, a water-resistant binder-shaped body provided as a non-polluting recyclable material can be prepared by being subjected to a shaping process in which re-mudging is prevented.

本発明においては、ここに調製されたpH12が確保されている活性化混和物を2通りの活用方法があり、第一は該活性化混和物自身で形状化体を構成せしめて形状化処理物として自己完結型の原位置非成型品、耐水性粉粒体品ないしは形状加工成型品とする活用方法であり、第二は流動性のある活性化混和物を予め用意された応用対象素材に付着化して付着化体を構成せしめて付着化処理物として基材付着型の活性粉体結着品、基材積層複合品、顆粒群体集合品ないしは注充填一体化品とする活用方法である。  In the present invention, there are two methods of utilizing the activated admixture having a pH of 12 prepared here, and the first is that the activated admixture itself constitutes a shaped product to form a shaped product. As a self-contained in-situ non-molded product, water-resistant granular product or shape-processed molded product, the second is to attach a fluid activated admixture to a prepared application target material This is a utilization method in which an adhering body is formed and an adhering treatment product is used as a base-attached active powder binding product, a base material laminated composite product, a granule aggregate assembly product, or an injection filling integrated product.

いずれの活用方法を採択しても、活性化混和物、ないし形状化処理物または付着化処理物において活性化効果を発揮した活躍したアルカリ成分は、養生工程により固定化されてpH10未満が確保され、同時に耐水性で水中再泥化しない無害化処理および形状化処理が施される改質処理方法に付して、粉粒体、砂粒体、顆粒体、硬化・固化体、構造体、形状体、フイルム・膜状体、機能性保持被覆体、積層・塗布体、顆粒群集合体ないし注充填一体化体からなる原位置非成型品、耐水性粉粒体品、形状加工成型品、活性粉体結着品、基材積層複合品、顆粒群体集合品または注充填一体化品を提供することができる。  Regardless of which method is used, the active alkaline component that exerted the activation effect on the activated admixture, or the shaped or adhered product is immobilized by the curing process to ensure a pH of less than 10. At the same time, it is subjected to a modification treatment method that is water-resistant and does not re-mudging in water, and is subjected to a modification treatment method. In-situ non-molded product, water-resistant granular product, shape-processed molded product, active powder consisting of film / film-like body, functional holding coating, laminated / coated body, granule group aggregate or injection-filled integrated body A binding product, a base material laminated composite product, a granule aggregate assembly product, or an injection filling integrated product can be provided.

したがって、本発明の改質処理法により調製される結着形状体の特徴は、熱履歴シリケート、特に有害物質を共存している廃棄物類を改質対象素材として、この改質対象素材を活性化するために使用したアルカリ成分等は固定化してpH値が10未満の結着形状体に改質処理して、環境に二次公害を与えない廃棄物類の無公害型の再資源化資材として工業用資材、建築・土木資材、生活関連資材、植物育成資材、環境対応資材ないしは趣向活資材の用途に低価格で安定して供給できるところにある。  Therefore, the feature of the bound-shaped body prepared by the modification treatment method of the present invention is that the thermal history silicate, particularly wastes coexisting with harmful substances, is used as the material to be modified, and the material to be modified is activated. Non-polluting, non-polluting material for waste that does not cause secondary pollution to the environment by immobilizing the alkaline components used for conversion into a bound shape with a pH value of less than 10 It can be stably supplied at a low price for industrial materials, construction / civil engineering materials, life-related materials, plant-growing materials, environmentally friendly materials or preference materials.

さらに、有害化学物質を共存する熱履歴シリケートを改質対象素材として、少なくとも常温において改質処理剤、ないしは有害化学物質を共存する改質処理剤を活用する一連の作業工程からなる改質処理方法に付して、該熱履歴シリケートに共存する有害化学物質ならびにダイオキシン類をpH10未満が確保されて環境基準値以下の範囲に固定・不溶化された無害化処理が施され、同時に水中再泥化しない耐水性に形状化処理が施されている結着形状体を好適に提供することができる。しかも本発明技術においては、改質対象素材の存在が、改質対象素材が存在する原位置であれ、持ち込まれた位置であれ、本発明の改質処理技術を施すことが可能であることから、幅広い分野での廃棄物類等の改質対象素材をその存在する位置において、本発明の目的・用途、ならびに作業条件等に従い改質処理された結着形状体を提供することが可能となる。  Further, a reforming treatment method comprising a series of work steps utilizing a heat treatment silicate coexisting with harmful chemical substances as a material to be reformed, at least at room temperature, or using a reforming treatment agent coexisting with harmful chemical substances. In addition, harmful chemical substances and dioxins coexisting in the heat history silicate are subjected to a detoxification treatment in which a pH of less than 10 is ensured and fixed and insolubilized within the environmental standard value range, and at the same time, it is not re-mudged in water. It is possible to suitably provide a bound-shaped body that has been subjected to water-resistant shaping treatment. Moreover, in the technology of the present invention, it is possible to apply the reforming processing technology of the present invention regardless of whether the material to be reformed is the original position where the material to be reformed is present or the position where it is brought in. In addition, it is possible to provide a bound shape that has been modified according to the purpose / use of the present invention, work conditions, etc., at the position where the material to be modified such as wastes in a wide range of fields exists. .

各論
本発明によれば、原位置に存在して有害物質である有害元素群ないしダイオキシン類を環境基準値以上の量で共存して汚染する土壌地盤、軟弱地盤、道路・堤・法面ないし農地・宅地・工業用地・公共用地からなる熱履歴シリケートは、本発明一連の作業工程により原位置で有害物質共存の改質対象素材に改質処理剤を活用する一連の作業工程からなる改質方法に付して、該熱履歴シリケートが活性化活用されて外圧に変動性を示す程度に結着・硬化せしめて有用土壌地盤、軟弱地盤、道路・堤・法面ないしは農地・宅地・公共用地にからなる無公害型再資源化資材に無害化処理ならびに形状化処理が施されている原位置非成型品に改質されている結着形状体として提供することができる。
Detailed Description According to the present invention, soil ground, soft ground, roads, dams, slopes, or farmland that coexist and contaminate harmful elements or dioxins that are in-situ and present in an amount in excess of the environmental standard value.・ Heat history silicate consisting of residential land, industrial land, and public land is a reforming method consisting of a series of work processes that utilize a reforming treatment agent as a material to be reformed in the in-situ coexistence with the present invention series of work processes. In addition, the heat history silicate is activated and utilized to bind and harden to such an extent that the external pressure exhibits variability, and is useful for soil, soft ground, roads, dikes, slopes, farmland, residential land, and public land. It is possible to provide a binding shape body that has been modified into an in-situ non-molded product in which the non-polluting material for recycling is made harmless and shaped.

また本発明によれば、原位置に存在して有害元素群ないしダイオキシン類を環境基準値以上の量で共存して汚染されている土質土壌、建築・土木関連廃土、窯業関連廃物、ケイ酸塩系投棄廃棄物類、汚泥・底質・脱水ケーキ類、焼却灰類からなる熱履歴シリケートは、原位置で有害物質共存の改質対象素材に改質処理剤を活用する一連の作業工程からなる改質方法に付することにより、該熱履歴シリケートが活性化活用されて一軸圧縮強度で500KN/m以上の強度が確保されている無公害型再資源化資材に無害化処理ならびに形状化処理が施されている原位置における形状加工成型品に改質されている結着形状体として提供することができる。Further, according to the present invention, soil soil, architectural / civil engineering related waste, ceramic industry related waste, silicic acid, which is present in situ and contaminated with harmful elements or dioxins coexisting in an amount exceeding the environmental standard value. Thermal history silicates composed of salt-based dumping waste, sludge, bottom sediment, dehydrated cakes, and incineration ash are a series of work processes that utilize a modification treatment agent as a material to be reformed in the presence of harmful substances. By applying this reforming method, the heat history silicate is activated and utilized, and the harmless treatment and shaping of the non-polluting recyclable material with a uniaxial compressive strength of 500 KN / m 2 or more is secured. It can be provided as a bound-shaped body that has been modified into a shape-processed molded product at the original position where the treatment is performed.

本発明によれば、持込位置に存在して有害物質共存の粉粒体ないし含水体からなる熱履歴シリケートは、改質処理剤を活用する一連の作業工程からなる改質方法に付することにより、該熱履歴シリケートが活性化活用されて粉粒状態にある再生砂、再生土、再生骨材、流動化処理材、覆砂材、中込材、造成材、盛土材、築堤材、土壌改良材、客土材の群からなる土木用資材、また植栽用土、造園用資材、緑化基盤材、目土の群からなる植物育成資材からなる無公害型の結着形状体に無害化処理ならびに形状化処理が施されている耐水性粉粒体品に改質されている結着形状体として提供することができる。  According to the present invention, a thermal history silicate consisting of a granular material or water-containing body coexisting with harmful substances present at a carry-in position is subjected to a reforming method comprising a series of work steps utilizing a reforming treatment agent. The activated heat history silicate is activated and utilized to regenerate sand, reclaimed soil, reclaimed aggregate, fluidized material, sand covering material, sand-filled material, reclaimed material, embankment material, embankment material, soil improvement Detoxification treatment for non-polluting binding shaped bodies consisting of materials for civil engineering consisting of a group of timbers, guest soil materials, planting soil, landscaping materials, planting base materials, plant growing materials consisting of groups of joint soils, and It can be provided as a bound-shaped body that has been modified into a water-resistant granular product that has been subjected to a shaping treatment.

さらに本発明によれば、持込位置に存在して有害物質を共存する粉粒体ないし含水体からなる熱履歴シリケートは、該有害物質共存の改質対象素材に改質処理剤を活用する一連の作業工程からなる改質方法に付することにより、該熱履歴シリケートが活性化活用されて一軸圧縮強度で500KN/m以上の強度が確保されている水中で再泥化することのない耐水性で耐熱性の特定形状の硬化体、構造体、固化体、成型体ないし膜状体等、また不特定形状の粉粒体、砂状体、顆粒体、骨材状、形状体等からなる無公害型再資源化資材に無害化処理ならびに形状化処理が施されている形状加工成型品に改質されている結着形状体として提供することができる。Furthermore, according to the present invention, a thermal history silicate composed of a granular material or a water-containing body that exists at the carry-in position and coexists with harmful substances is a series of utilizing a modifying agent as a material to be reformed that coexists with the harmful substances. By applying to the reforming method consisting of the above work steps, the heat history silicate is activated and utilized, and a uniaxial compressive strength of 500 KN / m 2 or more is secured. It consists of hardened, structured, solidified, molded or membranous bodies with specific shapes that are heat-resistant and heat-resistant, and powders, sandy bodies, granules, aggregates, shapes, etc. of unspecified shapes It can be provided as a bound shape that has been modified into a shape-processed molded product in which a pollution-free recycling material is subjected to a harmless treatment and a shape treatment.

本発明の持込位置に存在する好適な改質対象素材としては、熱履歴シリケートであるケイ酸塩系化合物を少なくとも50質量%含有しており、有害物質を共存する人工合成品、有機質素材類の乾留灰・石炭灰・ゴミや汚泥の焼却灰等の灰類、焼却窯業系の土質廃棄物、高炉・製鋼のスラグ類、底質や処理脱水ケーキを含む含水泥土類、土壌・粘土・土壌地盤、生活・工業・土木資材類ないしは火山噴出物からなる群より選ばれる単独ないし2種以上の組み合わせの粉粒体または含水体を好適に挙げることができる。  As a suitable material to be modified present at the carry-in position of the present invention, an artificial synthetic product or organic material containing at least 50% by mass of a silicate compound which is a heat history silicate and coexisting with harmful substances Ash, such as incineration ash of coal, coal ash, garbage and sludge, soil waste from incineration ceramics, blast furnace and steelmaking slag, hydrous mud including bottom sediment and treated dewatered cake, soil, clay and soil Preferable examples include a single granular material or a hydrated body selected from the group consisting of ground, life / industrial / civil engineering materials or volcanic products.

焼却灰
勿論、本発明における改質対象素材として好適に選択される有機質素材類の乾留灰・石炭灰・ゴミや汚泥の焼却灰等の灰類は、焼却場等から排出される灰類にダイオキシン類ならびに溶出有害元素金属が共存してくるのが一般的である。また、これらの灰類の排出においては、灰類の排出に伴い塩素やソックス・ノックス等の酸性ガスを伴い排気ガスを汚染していることから、これら酸性ガスを捕捉するために石灰等が投入されており、回収される焼却灰類には20質量%以上のカルシヤ成分を含有している灰類も本発明改質対象素材として好適に選択できる。
Incineration ash Of course, ash such as dry distillation ash, coal ash, garbage and sludge incineration ash of organic materials that are preferably selected as the material to be reformed in the present invention is dioxin to ash discharged from incineration sites, etc. In general, metals and eluting harmful element metals coexist. In addition, since ash is discharged, ash is discharged and contaminated exhaust gas with acid gases such as chlorine, socks and knox, so lime is added to capture these acid gases. Thus, ash containing 20% by mass or more of a calcium component can be suitably selected as the material to be modified in the present invention.

本発明の改質処理技術によれば、改質対象素材となる焼却灰や焼却場周辺の汚染土壌等に必然的に共存してくるダイオキシン類を原位置で少なくとも常温で分解無害化できる現象は重要である。焼却灰等に共存するダイオキシン類が少なくとも常温で分解される現象と分解機構原理に関しては、上述した[本発明技術の概要]の項で詳細に説明したが、特別な高価な設備ならびに特別なエネルギーを消費することなく、本発明技術で分解無害化できる改質処理技術は経済的にも、社会的にも大変有効である。  According to the reforming treatment technology of the present invention, the phenomenon that dioxins inevitably coexisting with the incineration ash that is the material to be reformed or the contaminated soil around the incineration site can be decomposed and detoxified at least at ordinary temperature in situ. is important. The phenomenon in which dioxins coexisting with incineration ash etc. are decomposed at least at room temperature and the principle of the decomposition mechanism have been described in detail in the above-mentioned section [Summary of the technology of the present invention]. The reforming treatment technology that can be decomposed and rendered harmless by the technology of the present invention without consuming energy is very effective both economically and socially.

また持込位置に存在する前記灰類の中でも有害物質を共存する含リン焼却灰は、窒素成分やリン成分を含有している下水含水汚泥ケーキ類、必要に応じてファンクションメントの機能付与組成物である消臭剤類が併配合されている改質対象素材として扱うことが可能であり、該含リン焼却灰の改質対象素材は、本発明一連の作業工程により、共存有害物質に無害化処理が施され、また同時に粉粒体の改質対象素材を結着・硬化せしめて耐水性の耐熱性で植物育成材、緑化材、目土、客土類、盛土、造成土、中込材、土壌改良材等に形状化処理が施されている形状加工成型品に改質して耐水性の結着形状体として有効に供給することができる。  In addition, phosphorus-containing incinerated ash that coexists with harmful substances among the ashes present in the carry-in position is a sewage hydrous sludge cake containing a nitrogen component or phosphorus component, and if necessary, a function-imparting composition It is possible to treat as a material to be reformed that is mixed with deodorants, and the material to be reformed of the phosphorus-containing incinerated ash is made harmless to coexisting harmful substances by a series of work steps of the present invention. At the same time, the material to be modified of the granular material is bound and hardened by water resistance, heat resistance, plant growth material, greening material, joint soil, custom soil, embankment, reclaimed soil, interstitial material, It can be reformed into a shape-processed molded product in which a shape improvement treatment is applied to a soil improving material or the like, and can be effectively supplied as a water-resistant binding shape.

また、これらの焼却灰類は、含水の汚泥や底質(ヘドロ)等の水分調整剤としても有効である。例えば、悪臭を有する下水汚泥や農業集落汚泥等の汚泥類、また海域湾岸や湖沼・ダム等に堆積している底質(ヘドロ)等の水分を調整したいときに加熱処理等を採用すると悪臭への対策・処理が難しく、問題を抱えている。  Further, these incineration ashes are also effective as moisture adjusting agents such as water-containing sludge and sediment. For example, if you want to adjust the moisture of sludge such as sewage sludge with bad smell or agricultural settlement sludge, or sediment (sadro) accumulated in sea area bays, lakes, dams, etc. Measures and processing are difficult and have problems.

悪臭
このような場合、悪臭を有する含水汚泥に対して加熱処理等を採用することなく、悪臭を有する含水汚泥に対して水保水性の高い同類の焼却灰を加えて水分調製することができることから好ましい。しかも、悪臭を有する含水汚泥ならびに加える焼却灰改質対象素材として本発明の改質方法に付するときは、これらに共存する有害物質を同時に固定・不溶化ないしは分解して無害化処理を施すことができることから好ましい。
Bad odor In such a case, water can be prepared by adding similar incinerated ash with high water retention capacity to hydrated sludge having bad odor without adopting heat treatment etc. to the hydrated sludge having bad odor. preferable. Moreover, when it is subjected to the reforming method of the present invention as a water-containing sludge having a bad odor and an incineration ash modification target material to be added, harmful substances coexisting with these may be fixed, insolubilized or decomposed at the same time to be detoxified. It is preferable because it is possible.

耐熱火組成物もしくは断熱・保温組成物
さらに本発明形状加工成型品を調製させるに際して、選択された改質対象素材に対して、さらに本発明形状加工成型品の目的・用途に応じて各種の機能性を有する素材や資材類を必要に応じて本発明改質処理剤に予め付加・補足しておくこと、ならびに本発明混和物を調製時に別途添加配合しておくことが好ましい。例えば、本発明形状加工成型品に耐熱性・断熱性・保温性等を確保するために本発明改質処理剤に耐熱火組成物もしくは断熱・保温組成物等を予め配合された改質処理剤を選ぶこともできる。
Heat-resistant fire composition or heat insulation / heat-retaining composition In addition, when preparing the shape-processed molded product of the present invention, various functions according to the purpose and use of the shape-processed molded product of the present invention are selected for the material to be modified It is preferable to add or supplement a material or materials having properties to the modifying agent of the present invention in advance as necessary, and to add and blend the inventive blend separately during preparation. For example, in order to ensure heat resistance, heat insulation, heat retention, etc., in the shape processed molded product of the present invention, a modification treatment agent in which a heat resistant fire composition or a heat insulation / heat retention composition is pre-blended with the present modification treatment agent You can also choose.

不焼成煉瓦
したがって、本発明改質処理剤100質量部に対して、機能付与剤のファンクションメントである耐熱火組成物もしくは断熱・保温組成物を100質量部以上の量で添加補足されている複合改質処理剤を採択して、一連の作業工程からなる改質方法に付されて無害化処理ならびに形状化処理が施されて、改質対象素材類が原位置や現場で対象となる設備や施設に直接施工が可能な不焼成もしくは焼成された特定または不特定の耐熱・保温築炉材、セラミックス品、レンガ・耐火材・断熱材ないしは保温・断熱材として供給される形状加工成型品に好適に改質することができる。
Non-fired bricks Therefore, a composite supplemented with 100 parts by mass or more of a heat-resistant fire composition or a heat insulating / heat-retaining composition as a functioning agent of a function-imparting agent with respect to 100 parts by mass of the present modification treatment agent Adopting a modification treatment agent, it is applied to the modification method consisting of a series of work processes, detoxified and shaped, and the materials to be modified are in-situ or on-site. Suitable for non-fired or fired specific or unspecified heat- and heat-resistant building materials, ceramics, bricks, fire-resistant materials, heat-insulating materials or shape-processed molded products supplied as heat-insulating / heat-insulating materials that can be directly applied to the facility Can be modified.

また、本発明によれば、施工現場で形状化される不焼成ないしは製造工場で予め形状化されている特定形状または不特定形状の形状加工成型品である耐火・耐熱性の形状加工成型品としては、機能付加成分のファンクションメントである耐熱火組成物(例:マグネシヤ、カルシヤ、シリカ、アルミナならびに酸化物の複合物、さらに炭化ケイ素、窒化物等の非酸化物、各種結晶のケイ酸アルミニウム、ケイ酸カルシウムや石綿、バーミュキュライトやパーライト等)を50質量%以上配合の改質処理剤を活用させて形状化処理した保温・断熱体、不焼成セラミックス、不焼成レンガ、耐火体もしく耐熱・不燃体からなる耐火・耐熱性の活用品が、有害物質を含有せず、水溶出pHが10未満であり、耐水性で一軸圧縮強度で1000KN/m以上であり、耐熱性強度保持率が少なくとも80%以上の確保される形状加工成型品に改質することができる。In addition, according to the present invention, as a fire-resistant / heat-resistant shape-processed molded product that is a non-fired shape formed at a construction site or a shape-processed molded product of an unspecified shape that is pre-shaped at a manufacturing factory. Is a heat-resistant composition that is a functional addition component (eg, a composite of magnesium, calcium, silica, alumina and oxide, non-oxides such as silicon carbide and nitride, aluminum silicates of various crystals, Insulation, heat insulation, non-fired ceramics, non-fired bricks, refractory bodies, etc. that are shaped by using a modifying agent containing 50% by mass or more of calcium silicate, asbestos, vermiculite, pearlite, etc. A fire-resistant / heat-resistant product made of heat-resistant and incombustible material does not contain harmful substances, has a water elution pH of less than 10, water-resistant and uniaxial compressive strength is 1000 KN / m It is 2 or more, and it can be modified into a shape-processed molded product that ensures a heat resistant strength retention of at least 80% or more.

したがって、本発明の耐水性の結着形状体においては、従来のセメントによる二次加工製品に替わって六価クロムを含有しない二次加工製品を製造することができると共に不焼成で耐熱性のある二次加工製品を少なくとも常温で、しかも施工現場で加工調製することができることから、従来窯業分野でエネルギーを多消費して焼き物として工場生産してきた窯業製品類(レンガ、断熱材、保温材等)の代替として、省エネで、二酸化炭素を放出することのなく環境に負荷を与えず環境に優しい方法により耐水性で耐熱性の例えば、不焼成のレンガや保温材等を加工調製することが可能である。  Therefore, in the water-resistant binder of the present invention, a secondary processed product not containing hexavalent chromium can be produced in place of the conventional secondary processed product with cement, and it is non-fired and heat resistant. Since the secondary processed products can be processed and prepared at least at room temperature and at the construction site, ceramic products (brick, heat insulating materials, heat insulating materials, etc.) that have been traditionally produced in the ceramic industry as a pottery with high energy consumption. As an alternative, it is possible to process and prepare water-resistant and heat-resistant materials such as unfired bricks and heat insulation materials by an environmentally friendly method that saves energy, does not release carbon dioxide, and does not cause environmental impact. is there.

本発明技術によれば、持込位置で有害物質共存の改質対象素材に施されるときの改質処理剤に対して、改質処理剤からなる改質処理剤100質量部に対して、機能付加成分ファンクションメントの断熱・保温組成物、または10m/g以上の比表面積を有し0.05ないし1.2g/ccの範囲にあるかさ密度を有し、耐熱性の繊維状または粉粒体状のシリケートもしくはケイ酸塩組成物からなるケイ酸カルシウム系化合物ないし保温・断熱材の廃材を100質量部以上の量で添加補足されている改質処理剤を採択して、本発明の一連の作業工程からなる改質方法により無害化処理が施される。According to the technology of the present invention, with respect to the modification treatment agent when applied to the modification target material coexisting with harmful substances at the carry-in position, with respect to 100 parts by mass of the modification treatment agent composed of the modification treatment agent, Heat-insulating / warming composition of functional addition component, or heat-resistant fibrous or powder having a specific surface area of 10 m 2 / g or more and a bulk density in the range of 0.05 to 1.2 g / cc Adopting a modification treatment agent supplemented with a calcium silicate compound comprising a granular silicate or silicate composition or a waste material of heat insulation / heat insulation material added in an amount of 100 parts by mass or more, The detoxification process is performed by a reforming method comprising a series of work steps.

また同時に粉粒体の改質対象素材を結着・硬化せしめて耐水性が確保され、一軸圧縮強度で100KN/m以上の強度が確保されている耐熱・保温築炉材、セラミックス体、耐火材・断熱材ないしは保温・断熱材に形状化処理が施されている結着形状化体である不焼成もしくは焼成された特定または不特定の保温・断熱材、セラミックス品、レンガ・耐火材・断熱材からなる形状加工成型品である耐水性の結着形状体が提供される。At the same time, the material to be reformed of the granular material is bound and cured to ensure water resistance, and the uniaxial compressive strength is 100 KN / m 2 or more. Non-fired or baked specified or unspecified heat-retaining / insulating materials, ceramic products, bricks, refractory materials, heat insulation Provided is a water-resistant binding shape body that is a shape-processed molded article made of a material.

フイルム状形状加工成型品
本発明によれば、持込位置に存在して有害物質を共存する改質対象素材を本発明の一連の作業工程に付することにより、予め調製された混和物であり糊状ないしは可塑状に調製されている流動性混和物をプラスチック製の基材・型類表面に1ないしは20mm厚の膜状、板状、塗膜状もしくはフィルム状の膜状物とし、養生工程において通常養生条件下で養生した後、基材・型類より脱着せしめ、共存有害物質に無害化処理が施され、また同時に粉粒体の改質対象素材を結着・硬化せしめて耐水性の耐熱性で不定形または定形の膜状、板状ないしはフイルム状処理体に形状化処理が施されている形状加工成型品からなる耐水性の結着形状体に改質することができる。
Film-shaped processed molded product According to the present invention, a blended material prepared in advance by subjecting a material to be modified that is present at the carry-in position and coexists with harmful substances to the series of work steps of the present invention. The flowable mixture prepared in the form of paste or plastic is formed into a film, plate, film, or film film having a thickness of 1 to 20 mm on the surface of the plastic substrate or mold, and the curing process. After being cured under normal curing conditions, it is desorbed from the base material and molds, the coexisting harmful substances are detoxified, and at the same time, the material to be modified of the granular material is bound and hardened to make it water resistant. It can be modified into a water-resistant binder-shaped body made of a shape-processed molded product in which a heat-resistant, irregular or regular film-like, plate-like or film-like treated body is subjected to shaping treatment.

含水底質類
また、持込位置に存在して有害物質を共存する含水底質類または上水・下水汚泥類からなる改質対象素材である汚泥類もしくは底質類の含水比が150より大きいときは、必要に応じて予め含水比を150未満に脱水処理し、さらに狭雑物があるときは狭雑物を予め除去処理する前処理工程により調整されている改質対象素材は、本発明一連の作業工程により、共存有害物質に無害化処理が施され、同時に粉粒体の改質対象素材を結着・硬化せしめて耐水性の耐熱性で硬化品、構造品、固化品、成型品もしくは膜状品もしくは不特定形状の形状加工成型品である顆粒品もしくは骨材状品に形状化処理が施されている形状加工成型品からなる耐水性の結着形状体に改質することができる。
Hydrous sediments Also, the moisture content of the hydrous sediments that are present at the carry-in location and coexist with harmful substances, or sludges or sediments that are materials to be reformed consisting of water and sewage sludge is greater than 150. In some cases, the material to be reformed that has been adjusted by a pretreatment step in which the water content ratio is dehydrated to less than 150 in advance as necessary, and when there is a contaminant, the contaminant is removed in advance. By a series of work processes, the coexisting harmful substances are detoxified, and at the same time, the material to be modified of the granular material is bound and cured, and it is cured, structured, solidified, and molded with water resistance and heat resistance. Alternatively, it can be modified into a water-resistant binding shape body consisting of a shape-processed molded product in which a granule product or an aggregate-shaped product that is a film-shaped product or a shape-processed molded product of an unspecified shape is subjected to a shaping process. it can.

含水底質類
勿論、貧酸素化して水域底部に存在する底質を浚渫し、その浚渫現場において浚渫された含水底質に本発明改質処理剤を加え、例えば砂粒状の顆粒物や構造体物等として、この顆粒物や構造体物等を底質の存在していた水域に戻して放置する養生工程に付し、酸素供給能力を有し、一定強度を有する顆粒状の活用品とし、しかも水域を汚さないpH値8.5未満で共存していた有害物質が無害化されている水域底部形成材料に形状化処理することにより、その結着形状体を水域中で生態系に悪影響を与えない耐水性の結着形状体として好適に提供することができる。
Hydrous sediments Of course, the bottom sediment present at the bottom of the water area is deoxygenated, and the modified treatment agent of the present invention is added to the hydrous sediment deposited at the dredging site, for example, sand granular granules and structures. For example, the granules and structures are subjected to a curing process in which they are returned to the water area where the sediment was present and left to stand, and are used as granular products having oxygen supply capacity and constant strength. It does not adversely affect the ecosystem in the water area by shaping the water bottom forming material in which the harmful substances coexisting at a pH value of less than 8.5 are made harmless. It can be suitably provided as a water-resistant binding shape.

また、含水の底質もしく上水・下水の汚泥である改質対象素材は、水分散の含水土質・汚泥・アオコ・藻類群からなる浮遊物を伴って、水中に分散状態で浮遊分散しているときは、前記のファンクションメントである沈降凝集組成物等を水中に浮遊分散している浮遊物に対して撒布して加え撹拌して、水分散性の浮遊物を水中で予め凝集沈降せしめ、水中底部底質として回収した改質対象素材としてから、本発明の一連の作業工程に付して、耐水性の結着形状体に改質することができる。  In addition, the material to be modified, which is the bottom sediment of water and sludge of water and sewage, floats and disperses in water in a dispersed state with suspended matter composed of water-dispersed soil, sludge, blue-green and algae. If this is the case, the function aggregation, such as the sedimentation aggregate composition, is applied to the suspended matter that is suspended and dispersed in water, stirred, and the water-dispersible suspended matter is then aggregated and settled in water in advance. The material to be reformed recovered as the bottom sediment in the water can be subjected to a series of work steps of the present invention to be modified into a water-resistant binding shape.

本発明結着形状体の形状加工成型品である硬化体、構造体、固化体、成型体ないし膜状体等の具体的な一例を示せば、容器類、U字溝、土管、フューム管、漁礁、テトラポット状、基礎石、インターロッキング、レンガ、内装・仕切・間仕切板、瓦、外壁、建材類、鉢類、置物、飾り物、装飾品、美術品、保護材、枕木、ベンチ、机、陶磁器、衛生陶器類、従来の窯業製品に代替できる分野では、特にレンガ・耐火材類、耐熱材料、タイル類、容器類、鉢類、建材、瓦、磁器、陶器類、飾物・置物、膜物、フイルム等、その他特定に成型・構造化されている形状加工成型品類等を好適に挙げることができる。  Specific examples of the cured body, structure, solidified body, molded body or film-like body that are the shape-processed molded product of the binding shape of the present invention include containers, U-shaped grooves, earthen pipes, fume pipes, Reef, tetrapot, foundation stone, interlocking, brick, interior / partition / partition plate, tile, outer wall, building materials, pots, figurine, ornaments, ornaments, art, protective material, sleepers, bench, desk, In fields that can replace ceramics, sanitary ware, and conventional ceramic products, especially bricks, refractory materials, heat-resistant materials, tiles, containers, pots, building materials, tiles, porcelain, ceramics, ornaments and figurines, film objects Favorable examples include shape-processed molded products that are specifically molded and structured, such as film and the like.

また、本発明耐水性の結着形状体群である形状加工成型品の不特定形状の粉粒体、砂状体、顆粒体、骨材状、形状体等の具体的な一例を示せば、球状・中空状・角状・箱状・棒状・柱状・管状・線状・繊維状・板状・瓦状・壁状等の顆粒体、骨材体、固結吸着体等やその他の不定形形状体等であり、砂利・砂代替、骨材、盛土、中込材、干潟等造成土、植栽土、充填材、粟オコシ状形状体の基材(保温材、断熱材、保水材、遮蔽材、防音材、脱臭材、清浄剤、抗微生物剤等)、触媒、廃棄物類等に形状化処理されている形状加工成型品等を好適に挙げることができる。  In addition, if a specific example of an unspecified powder, sand, granule, aggregate, shape, etc. of the shape-processed molded product that is the water-resistant binding shape group of the present invention, Spherical, hollow, square, box, rod, column, tube, wire, fiber, plate, tile, wall, etc., aggregates, aggregates, adsorbents, and other irregular shapes Shaped bodies, such as gravel / sand substitutes, aggregates, embankments, medium-filled materials, tidal flats, planting soil, fillers, base materials for cocoon-shaped bodies (heat insulating materials, heat insulating materials, water retaining materials, shielding) Preferred examples include shaped processed molded products that have been shaped into materials, soundproofing materials, deodorizing materials, detergents, antimicrobial agents, etc.), catalysts, wastes, and the like.

付着化処理物
本発明においては、付着化処理物を経て調製される活性粉体結着品、基材積層複合品、顆粒群体集合品ないしは注充填一体化品等に採択される応用対象基材は、無機質材質、岩石・粘土材質、水和鉱物材質、セラミックス・窯業材質、金属材質、木材質、繊維材質、有機質材質ないしはこれら材質の複合材質等からなる粉粒体、吸着性粉粒体、砂粒体、顆粒体、造粒体、硬化・固化体、構造体、床体、柱状体、管状体、線状体、板状体、膜状体、ガラクタ体ないしは形状化体等の中かから適宜好適に選ぶことができる。
In the present invention, in the present invention, an application target base material that is adopted as an active powder binder, a base material laminated composite product, a granule aggregate assembly product, or an injection-filled integrated product, etc. prepared through the adhesive treatment product Is an inorganic material, rock / clay material, hydrated mineral material, ceramics / ceramics material, metal material, wood material, fiber material, organic material or composite material of these materials, adsorbent powder material, From among sand granules, granules, granulated bodies, hardened / solidified bodies, structures, floor bodies, columnar bodies, tubular bodies, linear bodies, plate bodies, film bodies, junk bodies or shaped bodies, etc. It can be suitably selected appropriately.

予め混和工程で調製した可塑性ないしは流動性の活性化混和物を結着・固結・接着剤として、本発明の目的用途に応じて選ばれた応用対象基材の基材類表面に対して、塗装、接着、付着、結着、被覆、多層塗り、どぶ浸け、まぶし、貼り付け、塗りつけ、吹き付け、流し込み、注入等の加工付着手段により付着化加工処理されて塗布物、被覆物、付着物、結着物、床状物、積層物、注入一体化物等の付着化処理物とし、次いで養生工程を付することにより、基材付着型の活性粉体結着品、基材積層複合品、顆粒群体集合品ないしは注充填一体化品からなる結着形状体を調製することができる。  As a binder / consolidation / adhesive using a plastic or flowable activated admixture prepared in advance in the mixing process, the substrate surface of the base material to be applied selected according to the intended use of the present invention, Coating, adhesion, adhesion, binding, coating, multilayer coating, soaking, gliding, pasting, painting, spraying, pouring, pouring, etc. By applying an adhesion-treated product such as a binder, a floor-like material, a laminate, and an injection-integrated product, followed by a curing process, the substrate-attached active powder binder, the substrate laminate composite, and the granular mass It is possible to prepare a bound shape made of an aggregate product or a cast-filled integrated product.

活性粉体結着品
本発明によれば、比表面積100m/g以上を有する炭類、非晶質シリカ、活性ケイ酸、活性ケイ酸塩、珪藻土、活性アルミナ、活性なアルミノケイ酸塩化合物、含炭素乾留品、吸着性焼却灰ないしはゼオライトの群より選ばれる単独ないし2種以上の組み合わせ吸着性粉粒体を応用対象基材として、該応用対象基材表面に予め混和工程で調製された可塑状、マヨネーズ状、糊状ないしはスラリー状の流動性活性化混和物を付着・被覆・結着して付着化処理物とする加工工程を経る一連の作業工程に付することにより、有害化学物質を共存して粉粒体の該熱履歴シリケートが、吸着性が確保された不特定形状の粉粒体、顆粒体ないし形状化体からなる応用対象基材と固結一体化されている結着形状体に改質処理する改質処理方法を提供することができる。
Active powder binder product According to the present invention, charcoal having a specific surface area of 100 m 2 / g or more, amorphous silica, activated silicic acid, activated silicate, diatomaceous earth, activated alumina, active aluminosilicate compound, A plastic containing a carbon-containing carbonized product, an adsorbent incinerated ash, or a single or a combination of two or more kinds of adsorbent powders selected from the group of zeolites as an application target base material and prepared in advance in the mixing step on the surface of the target base material By attaching, coating, and binding fluidity-activated admixtures in the form of paste, mayonnaise, paste, or slurry, the process of passing through the processing process to make the treated product becomes an adhering chemical substance. Cohesive shape in which the heat history silicate of the powder and particles coexist is solidified and integrated with the base material to be applied consisting of powder, granule, or shaped body of unspecified shape with ensured adsorptivity Modification process to modify the body The method can be provided.

特に、比表面積25m/g以上である吸着性ないし反応性を有する粉粒体、またはファンクションメントである担持吸着組成物を処理対象として、必要に応じて予め水を含浸する粉粒体であり、具体的にはシリカゲル、アルミナゲル、活性炭、ゼオライト、珪藻土、粘土類等、さらに農業・林業・畜産・水産の分野から廃出される各種有機化合物や動植物の有機質素材、発酵分野、造園等の剪定廃材や間伐材、紙・パルプ分野、繊維・布分野、各種プラスチックス等から排出される有機質素材類を焼却または乾留焼却して回収されて吸着性を確保して、有害物質である重金属類やダイオキシン類を共存する吸着性ないし反応性を有する粉粒体からなる処理素材は、本発明一連の作業工程により、共存有害物質に無害化処理が施され、吸着性粉粒体が固結一体化された特定ないし特定形状体の活性粉体結着品からなる耐水性の結着形状体に改質することができる。In particular, it is an adsorbent or reactive powder having a specific surface area of 25 m 2 / g or more, or a granule that is impregnated with water in advance if necessary with a supported adsorbent composition that is a functionment. Specifically, silica gel, alumina gel, activated carbon, zeolite, diatomaceous earth, clays, etc., and various organic compounds discarded from the fields of agriculture, forestry, livestock and fisheries, organic materials of animals and plants, fermentation fields, landscaping, etc. Organic materials discharged from waste and thinned wood, paper / pulp field, textile / cloth field, various plastics, etc. are recovered by incineration or dry distillation incineration to ensure adsorptive properties, The processing material consisting of adsorbent or reactive powder that coexists with dioxins is subjected to the detoxification treatment for the coexisting harmful substances by the series of work steps of the present invention, and the adsorption is performed. Granular material can be modified to the water resistance of the binder-shaped body composed of the active powder binder products specific to the particular shape body that is consolidated integrated.

活性粉体結着品における穴埋め
本発明一連の作業工程の混和工程において、比表面積や細孔が確保されて吸着性もしくは反応性を有する活性粉体結着品を調製するには、吸着性または反応性を有する粉粒体の改質対象素材、特に焼却素材や乾燥素材に対して、予め必要な水系溶媒を含浸させて、活性粉体結着品に必要な吸着性または反応性の拠点となる比表面積や細孔を水で覆い詰めて確保されている状態を確保されている粉粒体に、一連の作業工程により、共存有害物質に無害化処理が施され、また同時に粉粒体の改質対象素材を結着・硬化せしめて耐水性の耐熱性で特定形状体ないし特定形状体で吸着性もしく反応性の確保されている活性粉体結着品からなる耐水性の結着形状体に改質することができる。
Filling holes in active powder binders In the mixing step of the series of work steps of the present invention, in order to prepare an active powder binder having adsorbability or reactivity with a specific surface area and pores secured, Reactive materials to be modified, especially incineration materials and dry materials, are impregnated with the necessary aqueous solvent in advance, and the adsorbent or reactive base necessary for the active powder binder The specific surface area and pores covered with water are treated with detoxification treatment for coexisting harmful substances through a series of work steps, and the granular material is secured. A water-resistant binding shape consisting of an active powder binding product that has a specific shape or specific shape, and is adsorbed or reactive with water resistance and heat resistance by binding and curing the material to be modified. The body can be modified.

基材積層複合品
また、本発明によれば、持込位置で有害物質を共存する粉粒体・含水体からなる改質対象素材が付着・結着力を有するペースト状、マヨネーズ状、モルタル状、糊状、可塑状ないしスラリー状の流動性混和物を活用して、加工工程において予め用意された無機質資材、岩石・粘土類、窯業資材、木、繊維質、有機質、金属ないしはこれら素材の複合素材により形成されている成型体、造成体ないし型類体等を応用対象基材として、その基材類表面に該流動性混和物を塗装、接着、結着、被覆、多層塗り、どぶ浸け、まぶし、貼り付け、塗りつけ、吹き付け、流し込み、注入手段により塗布・被覆・結着せしめて積層加工層を形成複合せしめ、塗布物、被覆物、付着物、結着物、床状物または積層物からなる基材積層複合物に調製することができる。
In addition, according to the present invention, the material to be reformed consisting of a granular material and a water-containing body that coexist with harmful substances at the carry-in position has a paste shape, mayonnaise shape, mortar shape, Utilizing paste-like, plastic-like or slurry-like fluid admixture, inorganic materials, rocks / clays, ceramic materials, wood, fiber, organic, metal, or composite materials of these materials prepared in advance in the processing process As a base material to be applied, the fluid mixture is applied, bonded, bonded, coated, multilayered, soaked, and dipped onto the surface of the base material. , Applying, coating, spraying, pouring, applying, coating and binding by injection means to form a laminated processed layer, and composite, coating, coating, deposit, binder, floor or laminate Preparation of laminated material composite Can be made.

調製された基材積層複合物を養生工程において、常温ないし100℃の雰囲気中に少なくとも15分間解放して反応・養生せしめる本発明一連の作業工程により、有害物質共存い無害化処理が施され、また同時に粉粒体の改質対象素材を基材に積層複合結着して剪断破壊付着力が200KN/m以上の付着力で確保された耐水性で耐熱性の塗布品、被覆品、付着品、結着品、床状品、積層品もしくは付着・結着品に形状化処理が施されている基材積層複合品からなる耐水性の結着形状体に改質することができる。In the curing process, the prepared substrate laminate composite is subjected to a detoxification treatment in the presence of toxic substances by the series of work steps of the present invention in which the reaction and curing are performed in an atmosphere of room temperature to 100 ° C. for at least 15 minutes. At the same time, the material to be modified of the granular material is laminated and bonded to the base material, and the shear fracture adhesion strength is secured with an adhesion strength of 200 KN / m 2 or more. Products, binders, floors, laminates, or bonded / bundled articles can be modified into a water-resistant binder-shaped body made of a substrate laminate composite.

本発明における結着・結着力を有する流動性混和物を塗布・結着せしめて複合型の耐水性の結着形状体として処理調製するときに採択される基材類としては、セメント等の水硬性二次製品、窯業製品、岩石等の無機質製、木製、繊維質製、有機質製、金属・合金製ないしはこれらの素材が複合された素材、成型物ないしは型類等を好適に選択して複合型耐水性の結着形状体を処理調製することができる。さらに、本発明で処理対象物とされる改質対象素材を対象に本発明改質処理剤を活用して処理調製された各種の特定形状品を当然ながら基材積層複合品の基材類とすることができる。  The base materials adopted when the fluid admixture having binding / binding force in the present invention is applied and bound to prepare a composite water-resistant binding shaped body include water such as cement. Hard materials, ceramic products, minerals such as rocks, wood, fibers, organic materials, metals / alloys, or a combination of these materials, moldings or molds, etc. A mold water-resistant binding shaped body can be prepared by treatment. Furthermore, of course, various kinds of specific shaped products prepared by utilizing the modifying treatment agent of the present invention for the material to be modified, which is the treatment object in the present invention, can do.

本発明による基材積層複合品である無公害型結着形状体の具体的な例としては、接着剤、バインダー、目地材、コーキング材、埋め物材、絡め材、捨てコン材、固め材、裏打ち材、アンカー材、コーティング材、粒・顆粒体等の表面まぶし剤、多層膜形成材、被覆材、床材、壁材、防水幕材、塗料、塗膜、各種機能膜(抗菌性、消臭性、結露防止性、磁気性、発光性、発色性、抗酸化性、発熱性、熱伝導性、絶縁性、紫外線・近赤外・赤外線吸収性、電磁波吸収性、芳香性、殺虫性、忌避性等)を挙げることができる。  Specific examples of the pollution-free binding shaped body that is a base material laminated composite product according to the present invention include an adhesive, a binder, a joint material, a caulking material, a filling material, an entanglement material, a discarded material, a hardening material, Backing materials, anchor materials, coating materials, surface spraying agents such as granules and granules, multilayer film forming materials, coating materials, flooring materials, wall materials, waterproof curtain materials, paints, paint films, various functional films (antibacterial, antibacterial Odor, anti-condensation, magnetic, luminous, coloring, antioxidant, exothermic, thermal conductivity, insulating, ultraviolet, near infrared, infrared absorbing, electromagnetic wave absorbing, aromatic, insecticidal, Repellency etc.).

前記の流動性混和物からなる糊状結着剤が、前記組成式(1)もしくは(2)で表されるケイ酸アルカリからなるアルカリソルトを構成成分とする粉粒体ないし水混和体からなる改質処理剤で調製される糊状結着剤自身を形状加工成型物に形状化せしめるか、または基材類表面に塗布・被覆・結着せしめて積層加工層を形成複合せしめる一連の作業工程により、pH4の酸性溶液に浸漬したときの固化体強度保持率が少なくとも80%確保されている耐酸性の形状加工成型品ないしは基材積層複合品に形状化処理ならびに無害化処理されている耐水性の結着形状体に改質することができる。  The pasty binder composed of the fluid admixture comprises a powder or water admixture comprising an alkali salt composed of an alkali silicate represented by the composition formula (1) or (2) as a constituent component. A series of work steps in which the paste-like binder itself prepared by the modifying treatment agent is shaped into a shape-processed molded product, or is applied, coated, and bonded to the surface of a substrate to form a laminated processing layer and combine it Thus, the acid-resistant shape-processed molded product or the substrate laminate composite product in which the solidified body strength retention rate is secured at least 80% when immersed in an acidic solution of pH 4 is formed and detoxified. It can be modified to a binding shape.

本発明による耐酸性の結着形状体は、不燃性・耐熱性の無機質であり、常温で施工性が可能であることから、食品工場、化学往生、厨房等の耐酸床材として有効である。また、酸性サイドにある温泉場等における水路や床材等として有効である。本発明の耐酸材料に好適な改質処理剤は、耐酸性が求められることから、硬化・固化強度を損なわない範囲で耐酸性に乏しいカルシヤ等の配合量は抑え、ケイ酸塩からなる水和鉱物を中心とするマトリックスで形成されるよう改質処理剤の組成内容を選ぶ必要がある。  The acid-resistant binder-shaped body according to the present invention is an incombustible and heat-resistant inorganic substance, and can be constructed at room temperature. Therefore, it is effective as an acid-resistant flooring material for food factories, chemical transfer, kitchens, and the like. It is also effective as a waterway or flooring in a hot spring resort on the acidic side. The modification treatment agent suitable for the acid-resistant material of the present invention is required to have acid resistance, so the amount of calcium and the like that has poor acid resistance is suppressed within a range that does not impair the hardening and solidification strength, and hydrated from silicate. It is necessary to select the composition of the modifying agent so that it is formed of a matrix centered on minerals.

さらに本発明による結着形状体は、基本的に耐水性で耐熱性であることから、本発明基材積層複合品においても積極的に耐熱性資材類(レンガ、耐火材、保温剤、断熱材、耐熱建材等]に活用することができる。しかも、本発明混和工程で調製される活性化混和物は、耐熱性資材類の求められている現場の原位置で、対象とする素材に併せて現場で施工して耐熱性資材類を調製することができることから好ましい。  Furthermore, since the bonded shaped body according to the present invention is basically water-resistant and heat-resistant, the heat-resistant materials (brick, refractory material, heat-retaining agent, heat-insulating material) are also actively used in the base-material laminated composite product of the present invention. In addition, the activated admixture prepared in the blending process of the present invention is in-situ at the site where heat-resistant materials are required, and is combined with the target material. It is preferable because it is possible to prepare heat-resistant materials by construction on site.

顆粒群体集合品
本発明一連の作業工程により調製された顆粒状・骨材状の集合群体、または既存の無機質で粒径が2ないし12mmφでかさ密度が0.2ないし3.5g/ccの球状、中空状、円柱状、フレーク状、顆粒状、不特定粒状、骨材状、不特定粒状、ガラクタ状または粉粒状集合群体類を応用対象基材として、これらの顆粒集合群体類の基材表面を本発明の流動性混和物を結着剤として顆粒群体が集合して一体化された例えば粟お越し状の顆粒群体集合品を調製することができる。
Granule group aggregate product Granular / aggregate aggregate group prepared by a series of working steps of the present invention, or an existing inorganic sphere having a particle size of 2 to 12 mmφ and a bulk density of 0.2 to 3.5 g / cc, Hollow, cylindrical, flaky, granular, unspecified granular, aggregated, unspecified granular, garlic or granular aggregates are used as target substrates, and the substrate surface of these granular aggregates is For example, a granule aggregate assemblage in which the granule aggregates are aggregated and integrated by using the fluid mixture of the present invention as a binder can be prepared.

また、本発明によれば、持込位置に存在して有害物質を共存する改質対象素材は、本発明一連の作業工程により、前記の骨格素材を構成する集合群体の表面全体を濡らせる量で前記の流動性混和物からなる糊状結着剤を加え、群体粒子の表面全体を結着剤で被覆・決着せしめて集合群体を集合群体形状物とし、次いで集合群体形状物を常温ないし180℃雰囲気中に少なくとも10分間解放して反応・養生せしめ、共存有害物質に無害化処理が施され、また同時に粉粒体の改質対象素材を結着・硬化せしめて耐水性で耐熱性の集合群体が一体化した粟オコシ状活用品に形状化処理が施されている顆粒群体集合品からなる耐水性の結着形状体に改質することができる。  Further, according to the present invention, the amount of the material to be modified that is present at the carry-in position and coexists with the harmful substance wets the entire surface of the aggregate group constituting the skeleton material by the series of work steps of the present invention. Then, a paste-like binder composed of the above-mentioned fluid admixture is added, and the entire surface of the group particles is coated and settled with the binder to form the aggregate group into an aggregate group-shaped article, and the aggregate group-shaped article is then cooled to room temperature to 180. Release for at least 10 minutes in an atmosphere at ℃ for reaction and curing, detoxification treatment for coexisting harmful substances, and at the same time bind and harden the material to be reformed in granular form to make it water and heat resistant It can be modified into a water-resistant binding shape body consisting of a granular group aggregate product in which a shape processing is applied to a coconut-shaped utilization product in which the group body is integrated.

顆粒群体を粟オコシ状に集合一体化している顆粒群体集合品を構成する顆粒体の材質に関する具体的な例は、無機質のケイ酸塩、パーライト等の軽量材、コンクリート、金属類、焼き物、窯業製品、ガラス、溶融物、廃棄物類等、有機物の木、竹、繊維、紙、ゴム、プラスチック等、これらの複合品等の材質を挙げることができる。  Specific examples of granule materials that make up the granule aggregate assembly, in which the granule aggregates are gathered and integrated in the shape of a cocoon, include inorganic silicates, lightweight materials such as perlite, concrete, metals, pottery, and ceramics. Examples include materials such as products, glass, melts, wastes, organic wood, bamboo, fibers, paper, rubber, plastics, and composites thereof.

本発明に一連の作業工程により、耐水性で耐熱が確保され、pH10未満の低アルカリ性が確保され、無公害型が確保され、必要に応じて貫通空隙を有している粟オコシ状の集合体である顆粒群体集合品の具体的な例は、通気性、透水性、軽量性、重量性等を有している無機質で耐水性・耐熱性を有する各種液体のろ過体、浄化体等として、また気体の吸着体、触媒体、清浄体、保温材、活性材等として、防音壁材、緑化植物等の基材、建材類、土木資材等を好適に挙げることができ、例えば、液体や気体等の流動体を清浄したり、処理したり、化学変化を与えたりできるハニカムやキャリヤー等の基材として利用することも可能である。  A series of working steps according to the present invention ensures water resistance and heat resistance, ensures low alkalinity of less than pH 10, ensures a non-polluting type, and has an oak-like aggregate having through voids as necessary Specific examples of aggregates of granular aggregates are as various liquid filter bodies, purifiers, etc., which are inorganic and water-resistant and heat-resistant with air permeability, water permeability, light weight, weight, etc. Further, examples of gas adsorbers, catalyst bodies, clean bodies, heat insulating materials, active materials, and the like can include soundproof wall materials, base materials such as greening plants, building materials, civil engineering materials, etc., for example, liquid or gas It is also possible to use it as a substrate such as a honeycomb or a carrier that can clean, treat, or give a chemical change.

前記の集合群体が所定容器に収納されている容器収納ガラクタ集合群体を一体化処理対象のガラクタ集合群体として、一体化注入混和物が、乾燥物基準で表して持込位置に存在する有害物質を共存する改質対象素材100質量部に対して、改質処理剤を5ないし30質量部ならびに改質対象素材の含有水分を勘案して水系溶媒を全体で少なくとも50質量部以上の範囲で加えて全体を混和せしめてペースト状ないしスラリー状の流動性混和物、必要に応じてインプルーブメントのリン酸根組成物ないしバリウム塩組成物を配合して可使時間を調整した予め調製される流動性混和物を調製する。  A container-containing trash assembly group in which the assembly group is stored in a predetermined container is used as a galactor assembly group to be integrated. To 100 parts by mass of the reforming target material coexisting, 5 to 30 parts by mass of the modifying treatment agent and the water-based solvent are added in a range of at least 50 parts by mass in total considering the moisture contained in the reforming target material. Pre-prepared flowable mixture prepared by mixing the whole and mixing paste-like or slurry-like flowable mixture, and, if necessary, the phosphate group composition or barium salt composition of improvement to adjust the pot life. To prepare.

次いで上記のガラクタ集合群体の収納された容器に対して、該流動性混和物を注入充填し、必要に応じて攪拌注入充填して注充填形状物とし、次いで養生工程における常温ないしは180℃の雰囲気中に少なくとも10分間解放して反応・養生せしめることにより、無害化処理されて容器に収納された集合群体が容器内で一体化された注充填一体化体に形状化処理ならびに無害化処理が施されている注充填一体化品からなる耐水性の結着形状体に改質することができる。  Next, the fluid admixture is injected and filled into the container containing the above-mentioned junk aggregate assembly, and if necessary, the mixture is stirred and filled to form a pouring-filled shape, and then at an ordinary temperature or 180 ° C. atmosphere in the curing process. It is released for at least 10 minutes inside and allowed to react and cure, and then the shape filling process and the detoxification process are performed on the injection-filled integrated body in which the aggregate group that has been detoxified and stored in the container is integrated in the container. It can be reformed into a water-resistant binder-shaped body made of a cast-filled integrated product.

また、前記の集合群体が、低レベルの放射性物質からなる廃棄物類で調製されている集合群体であるときは、この低レベルの放射性物質からなる集合群体を容器に収納した集合群体として、該容器に収納された集合群体を遠隔操作を可能とする一連の作業工程により、容器収納集合群体中に前記の流動性混和物を容器中に空隙を残さないように注意して注入充填して注充填一体化品とし、無害化処理ならびに一体化した形状化処理されている耐水性の結着形状体に安全に活用処理することができる。  Further, when the aggregate group is an aggregate group prepared with wastes composed of low-level radioactive substances, the aggregate group composed of the low-level radioactive substances contained in a container, Through a series of work steps that enable remote operation of the collective assembly stored in the container, the fluid admixture is poured into the container-contained collective assembly with care so as not to leave a void in the container. It is possible to safely utilize and process a water-resistant binding shape body that has been made harmless treatment and integrated shaping treatment, as an integrated product.

[物性評価試験方法]
本発明においては、本発明に係る改質処理素材、改質処理剤ならびに耐水性の結着形状体類の諸物性・性能等を評価するため、下記に示すそれぞれに対応する試験・分析方法を採択して行った。
[Physical property evaluation test method]
In the present invention, in order to evaluate various physical properties and performance of the modified treatment material, the modified treatment agent and the water-resistant binder-shaped bodies according to the present invention, test and analysis methods corresponding to the following are provided. It was adopted.

本発明の物性評価試験における各試験体の標準的作成方法ならびに測定・分析は、下記に示した手順・方法によってそれぞれ行った。
なお、本明細書においては『部』および『%』の記載は、特記しない限り「質量」を以って示し、容量リッターの表示記載を『L』を以って表示することがある。
The standard preparation method and measurement / analysis of each specimen in the physical property evaluation test of the present invention were performed according to the following procedures / methods.
In the present specification, “part” and “%” may be indicated by “mass” unless otherwise specified, and the capacity liter display may be indicated by “L”.

01.円柱状試験体ならびに顆粒状試験体の調製
本発明技術における「水溶出pH値」「耐水性」「耐熱性」「一軸圧縮強度」「顆粒体強度」「付着力」等の試験に供する試験体は、各実施例で特記しない限り下記に示す標準手順で作成した円柱状ないしは顆粒状の標準試験体を供試体とした。
01. Preparation of cylindrical specimen and granular specimen Specimens used for tests such as "water elution pH value", "water resistance", "heat resistance", "uniaxial compressive strength", "granular strength", and "adhesion" Unless otherwise specified in each example, a cylindrical or granular standard test specimen prepared by the standard procedure shown below was used as a specimen.

円柱状の試験体は、各実施例記載の配合内容により全体を均質に混和して可塑性ないしは流動性に調製され混和物とし、該混和物をφ50×100mmの円柱状プラスチック製の容器(参照:JISR5201)に注入充填し、表面をビニールフイルムで覆って密封状態で特記しない限り28日間室温(約25℃)にて反応・養生した後脱型する手順で調製した。  The cylindrical test specimen is uniformly mixed to be plastic or fluid according to the blending contents described in each example to prepare an admixture, and the admixture is a cylindrical plastic container of φ50 × 100 mm (see: JISR5201) was injected and filled, and the surface was covered with a vinyl film, and unless otherwise specified in a sealed state, it was prepared by the procedure of demolding after reaction and curing at room temperature (about 25 ° C.) for 28 days.

顆粒状の試験体は、各実施例記載の配合内容により全体を均質に混和して可塑性ないしは流動性に調製され混和物とし、該混和物を粒径2ないし7mmφの顆粒状に造粒し、密閉可能なプラスチック製容器に入れ、特記しない限り28日間室温(約25℃)にて反応・養生して調製した。  The granular specimens were mixed uniformly according to the blending contents described in each example to prepare a plastic or flowable mixture, and the mixture was granulated into granules having a particle diameter of 2 to 7 mmφ. Unless otherwise specified, it was prepared by reacting and curing at room temperature (about 25 ° C.) for 28 days.

なお、顆粒状ならびに円柱状の試験体である「標準試験体」は、処理対象素材100質量部に対して、改質処理剤18質量部と水25質量部を加える配合を標準とし、全体を均質に混和して可塑状混和物を調製し、円柱状試験体では円柱状プラスチック製の容器内での密封状態の所定条件下で養生し、顆粒状試験体では顆粒物を所定条件下の開放状態で養生し、特記しない限り28日間室温(約25℃)に放置養生した試験体を標準試験体として。  In addition, “standard test body”, which is a granular and cylindrical test body, has a standard composition of adding 18 parts by mass of a modification treatment agent and 25 parts by mass of water to 100 parts by mass of a material to be treated. Homogeneously mix to prepare a plastic mixture, and in the case of a cylindrical specimen, it is cured under specified conditions in a sealed state in a cylindrical plastic container, and in the granular specimen, the granules are opened under specified conditions. Unless otherwise specified, test specimens allowed to stand at room temperature (about 25 ° C.) for 28 days as standard specimens.

02.水溶出pH値
水溶出pH値の測定は、所定条件下で調製した各試験体、処理対象素材、改質処理剤原料、改質処理剤、結着形状体等の供試料試験体10gを20℃でpH7の純水50gの入った容器に投入し、20℃で30分間攪拌して回収した溶出検液をpHメーターによりpH測定し、試験体の5質量倍水に対するサスペンジョン溶出検液におけるpH値として測定した。
02. Water elution pH value The measurement of water elution pH value is performed on 20 g of sample specimens such as test specimens prepared under predetermined conditions, materials to be treated, raw materials for modification treatment agents, modification treatment agents, and bound shapes. The elution test solution, which was put into a container containing 50 g of pure water at pH 7 at 50 ° C. and stirred for 30 minutes at 20 ° C., was measured for pH with a pH meter, and the pH in the suspension elution test solution for 5 mass-fold water of the test specimen was measured. Measured as a value.

03.耐水性の確認試験
耐水性の確認試験は、円柱状試験体ないしは顆粒状試験体を供試料として、円柱状試験体においては砕いて2ないしは10mm状の塊状物とし、これら塊状ないしは顆粒状試験体10gを水100gの入った容器に投入し、ゆっくりと30分間攪拌し、顆粒状試験体が顆粒状を維持して形状に崩れのない場合を耐水性「あり」と評価し、顆粒状試験体が崩壊もしくは泥状化による再泥化状態になる場合を耐水性「なし」と評価した。
03. Water resistance confirmation test The water resistance confirmation test was performed by using a cylindrical specimen or granular specimen as a sample, and crushing the cylindrical specimen into 2 or 10 mm aggregates, and these aggregate or granular specimens. 10g is put into a container containing 100g of water, and slowly stirred for 30 minutes. When the granular test specimen maintains the granular shape and does not collapse into the shape, the water resistance is evaluated as "Yes". The water resistance was evaluated as “None” when it became a re-mudified state due to collapse or mudification.

04.耐熱性の確認試験
耐熱性の確認試験は、所定条件下で調製した円柱状ないし顆粒状の試験体を600℃の電気加熱オーブン中に2時間放置暴露し、暴露後の試験体に異状がなく、一軸圧縮強度の強度維持率が50%以上である処理試験体を耐熱性「あり」と評価し、暴露後の処理試験体に異状があり、一軸圧縮強度の強度維持率が50%未満の処理試験体を耐熱性「なし」と評価した。
04. Heat resistance confirmation test In the heat resistance confirmation test, a cylindrical or granular specimen prepared under specified conditions is left exposed in an electric heating oven at 600 ° C for 2 hours, and the specimen after exposure is free from any abnormalities. A treated specimen having a strength retention ratio of uniaxial compressive strength of 50% or more was evaluated as “heat-resistant”, and the treated specimen after the exposure was abnormal, and the strength maintenance ratio of uniaxial compressive strength was less than 50%. The treated specimen was evaluated as “no heat”.

なお、耐熱性の確認試験における熱収縮減少率(%)は、長さ方向の寸法(Lo)の円柱状の試験体を600℃の電気加熱オーブン中に2時間放置暴露し、暴露後の試験体に異状ない試験体の長さ方向の寸法(La)を測定し、収縮減少を%で表した。  The heat shrinkage reduction rate (%) in the heat resistance confirmation test was determined by exposing a cylindrical specimen having a lengthwise dimension (Lo) in an electric heating oven at 600 ° C. for 2 hours, and then performing the test after exposure. The dimension (La) in the length direction of the test specimen that was not deformed on the body was measured, and the shrinkage reduction was expressed in%.

05.一軸圧縮強度試験
一軸圧縮強度試験は、JSCE F506およびJSCE G505記載の方法(コンクリート・モルタル試験法)に準拠して、標準試験体調製の項記載の円柱状試験体(φ5×10cm:n=3)を密閉状態で7日間常温に放置後、試験体を一軸方向で圧縮破壊強度(q)を測定し、この時の圧縮破壊強度(q)をKN/m単位で表示した。
05. Uniaxial Compressive Strength Test The uniaxial compressive strength test is a cylindrical specimen (φ5 × 10 cm: n = 3) described in the section of standard specimen preparation in accordance with the method (concrete mortar test method) described in JSCE F506 and JSCE G505. ) Was allowed to stand at room temperature for 7 days in a sealed state, and the specimen was measured for compressive fracture strength (q) in a uniaxial direction, and the compressive fracture strength (q) at this time was displayed in KN / m 2 units.

06.顆粒体の強度試験
顆粒体の強度試験は、3.標準試験体の調製の項記載の顆粒状試験体の中から選んだ粒径3〜5mmφ試験体9個を供試料とした。強度測定試験機は、2枚の厚さ2mmの鉄板(50×50mm)の4隅に鉄板の自重に耐える少なくとも7mmのスプリングを具備せしめ、2枚の鉄板の間隙中央に顆粒状の供試料1個をセットして、鉄板上部中央に分銅による荷重を加え、供試料顆粒体が崩れたときの荷重分銅の総重量を測定し、供試料9個の荷重重量の測定平均値を以って、供試料顆粒体の強度として評価した。
06. 2. Strength test of granule Nine specimens having a particle diameter of 3 to 5 mm selected from the granular specimens described in the section of preparation of standard specimen were used as samples. The strength measurement tester has at least 7 mm springs that can withstand its own weight at the four corners of two 2 mm thick steel plates (50 × 50 mm), and a granular sample 1 at the center of the gap between the two iron plates. Set a piece, apply a load with a weight to the upper center of the iron plate, measure the total weight of the load weight when the sample granule collapses, and with the average value of the load weight of nine samples, The strength of the sample granule was evaluated.

07.付着力の試験
本試験は、JIS K 6852に記載の方法に準拠して、30×25cmの鋼板と30×25cmで厚さ0.5mmのケイカル製スレート板との長方形試験片を3枚基材として、鋼板は240番の練研磨紙を用いて金属光沢が出るほどに磨き上げ、混合溶剤で洗浄して乾燥する。ケイカル製スレート板は水洗して乾燥する。
07. Adhesive strength test This test is based on a method described in JIS K 6852, which is a base of three rectangular test pieces of 30 × 25 cm steel plate and 30 × 25 cm and 0.5 mm thick slate made of calcium. Then, the steel plate is polished to such a degree that a metallic luster is produced using No. 240 kneaded abrasive paper, washed with a mixed solvent and dried. The calcium slate plate is washed with water and dried.

次いで、所定の活性化混和物を5mm厚で、表面を洗浄したケイカル製スレート板の長方形試験片基材の25×25cm面に塗布し、その上に鋼板で5mm厚の長方形の試験片基材の25×25cm面を対応させて載せる。この時、所定の活性化混和物が塗布されていない5×25cm部分を相互に反対部分直線上に耳状はみ出しさせてセットして付着力の試験体とする。付着力の試験体を所定条件下(例:20℃×28日間)に放置した後、圧縮強度試験機を用いて、試験体の耳状部分を立てて縦方向に加重を加え、そのときの剪断破壊力を加重速度による破壊強度(KN/m)を測定して付着力を評価した。但し、加重を加えた接着部でなく、基材のスレート部材が破壊したときは、基材材質強度を越える接着強度として評価した。Next, a predetermined activated admixture having a thickness of 5 mm was applied to a 25 × 25 cm surface of a rectangular test piece base of a slate plate made of calcium whose surface had been cleaned, and a rectangular test piece base having a thickness of 5 mm with a steel plate thereon. The 25 × 25 cm surface of is placed in correspondence. At this time, the 5 × 25 cm portion to which the predetermined activated admixture is not applied is protruded and set on a straight line opposite to each other to form a test specimen for adhesion. After leaving the test specimen for adhesive strength under predetermined conditions (eg, 20 ° C. × 28 days), using the compressive strength tester, the ear-shaped part of the test specimen was put up and weight was applied in the vertical direction. The adhesive strength was evaluated by measuring the shear strength (KN / m 2 ) at the load speed. However, when the slate member of the base material was broken rather than the adhesive part to which the load was applied, the adhesive strength exceeding the base material strength was evaluated.

08.引張荷重試験
試験方200mmを引張荷重試験機にて破壊迄の間、速度10mm/分にて加重をかけた時に破断したときの最大荷重(Kg)を測定して評価した。
08. Tensile load test The 200 mm test method was evaluated by measuring the maximum load (Kg) when ruptured by applying a load at a speed of 10 mm / min until breaking with a tensile load tester.

09.窒素分溶出試験
本発明における改質処理品類である結着形状体における窒素分の溶出測定は、底質調査方法の分析方法に準拠し、室内実験装置により一定の温度の確保できる円筒(φ10、高さ30cm)に供試料を採り、予め脱酸素された水を注ぎ、24時間放置した後、放置条件下で窒素分の溶出した水を採取し、窒素分が溶出する海水中の窒素分濃度を測定してmg/L単位で表示した。
09. Nitrogen content elution test The elution measurement of nitrogen content in the bound shaped body, which is a modified product in the present invention, is based on the analysis method of the bottom sediment investigation method, and a cylinder (φ10, Take a sample at a height of 30 cm), pour in water that has been deoxygenated beforehand, leave it for 24 hours, and then collect the water from which nitrogen content has been eluted under the standing conditions. Was measured and displayed in mg / L.

10.有害元素群の溶出試験
本発明においては、対象素材や活用品(試験体)における含有重金属類の主たる組成分析は、土壌分析法における底質調査方法IIに準拠して、主成分の分析は蛍光X線分析法により分析した。含有微量重金属類は、底質調査方法の分析方法に準拠した。
重金属類溶出量は、下記2種類のpH域溶出試験方法による検液を分析し測定した。
1中性域における溶出試験である環境省46号溶出試験法
2酸性域における溶出試験であるオランダNEN7341溶出試験法
10. In the present invention, the main compositional analysis of the heavy metals contained in the target material and the used product (test specimen) is based on the sediment analysis method II in the soil analysis method, and the analysis of the main component is fluorescent. Analysis was performed by X-ray analysis. Contained trace heavy metals conformed to the analysis method of the sediment survey method.
The amount of elution of heavy metals was measured by analyzing test solutions by the following two pH range elution test methods.
1 Dissolution test method of Ministry of the Environment No. 46 which is a dissolution test in neutral range 2 Dutch NEN7341 dissolution test method which is a dissolution test in acidic range

10−1環境庁告示46号溶出試験[略記:pH7溶出試験法:]
10−11試料の作成
採取供試料土壌を風乾し、中小礫、木片等を取り除き、土塊、団粒を粗砕した後、非金属製2mm目篩を通過させた土壌を十分混合する。
10−12試料液の調製
試料(g)と溶媒(純粋に塩酸を加え、水素イオン濃度指数が5.8以上6.3以下となるようにしたもの)とを重量比10%の割合で混合し、且つ、その混合液が500ml以上となるようにする。
10-1 Environmental Agency Notification No. 46 dissolution test [abbreviation: pH 7 dissolution test method]
10-11 Preparation of Samples Collected and sampled soil is air-dried, medium pebbles, wood chips, etc. are removed, clots and aggregates are crushed, and then the soil passed through a non-metallic 2 mm sieve is mixed thoroughly.
10-12 Preparation of sample solution Sample (g) and solvent (added with pure hydrochloric acid so that the hydrogen ion concentration index is 5.8 or more and 6.3 or less) are mixed at a ratio of 10% by weight. In addition, the mixed solution is made to be 500 ml or more.

10−13溶出
調製試料液を常温(おおむね20℃)常圧(おおむね1気圧)で振とう機(あらかじめ扱とう回数を毎分約200回に、振とう幅を4cm以上5cm以下に調整したもの)を用いて、6分間連続して振とうする。
10−14検液の作成
以上の操作による試料液を10分〜30分静置後、毎分約3,000回転で20分間遠心分離し、上澄液を孔径0.45μmのメンブランスフィルターでろ過してろ液を採り、定量に必要な正確な量を検液とする。
10-13 Elution Preparation Sample solution is shaken at room temperature (generally 20 ° C.) and normal pressure (generally 1 atm) (adjusted in advance to about 200 times per minute and shake width adjusted from 4 cm to 5 cm) ) And shake continuously for 6 minutes.
10-14 Preparation of test solution The sample solution by the above operation is allowed to stand for 10 to 30 minutes, then centrifuged at about 3,000 rpm for 20 minutes, and the supernatant is filtered with a membrane filter having a pore size of 0.45 μm. Filter to collect the filtrate, and use the exact amount required for quantification as the test solution.

10−2オランダNEN7341溶出試験[略記:pH4溶出試験法:]
10−21試料の作成
採取した供試料土壌を風乾し、中小礫、木片等を取り除き、土塊、団粒を粗砕した後、非金属製の2mm目のふるいを通過させて得た土壌を十分混合する。
10-2 Netherlands NEN7341 dissolution test [abbreviation: pH4 dissolution test method]
10-21 Preparation of sample The collected sample soil is air-dried, medium pebbles, wood chips, etc. are removed, the clot and aggregate are crushed, and then the soil obtained by passing through a non-metallic 2 mm sieve is sufficient. Mix.

10−22試料液の調製
試料16gに蒸留水800gを加え、1モル/Lの硝酸でpH7に調製しながら維持して3時間撹拌する。次いで、孔径0.45μmのメンブランスフィルターでろ過してろ液を取り、定量に必要な量を正確に計り取り、これをpH7溶出液とする。さらにpH7溶出のろ過残渣に蒸留水800gを加え、今度は1モル/Lの硝酸でpH4に調製しながら維持して3時間撹拌する。次いで、孔径0.45μmのメンブランスフィルターでろ過してろ液を取りpH4溶出液とする。
10−23検液の作成
以上操作を行って得られたpH7溶出液とpH4溶出液とを加え混合して、定量に必要な量を正確に計り取って、これを検液とする。
Preparation of 10-22 sample solution 800 g of distilled water is added to 16 g of the sample, and the mixture is maintained at pH 7 with 1 mol / L nitric acid and stirred for 3 hours. Next, the solution is filtered through a membrane filter having a pore diameter of 0.45 μm, and the filtrate is taken. The amount necessary for quantification is accurately measured, and this is used as a pH 7 eluate. Further, 800 g of distilled water is added to the pH 7-eluted filtration residue, and this time, while maintaining the pH at 4 with 1 mol / L nitric acid, the mixture is stirred for 3 hours. Next, the solution is filtered through a membrane filter having a pore diameter of 0.45 μm, and the filtrate is taken as a pH 4 eluate.
Preparation of 10-23 test solution The pH 7 eluate and pH 4 eluate obtained by the above operations are added and mixed, and the amount required for quantification is accurately measured, and this is used as the test solution.

11.簡易型変形性測定試験 (外圧変形性強度)
本試験は、本発明による処理土壌が有する変形性を評価するために、「標準貫入試験」に替えて、簡易型の変形性測定試験を採択した。本試験は、基本的にモルタル試験で採択されているJSCE F 506ならびにJSCE G 505の記載に準拠して混和物を円柱状試験体(φ5×10cm:n=3)に作成し、密閉状態で7日間常温に放置後、一軸方向の圧縮破壊強度(qu)をKN/m単位で測定して表示した。
11. Simple deformation test (external pressure deformation strength)
In this test, in order to evaluate the deformability of the treated soil according to the present invention, a simplified deformability measurement test was adopted instead of the “standard penetration test”. In this test, an admixture was prepared in a cylindrical test specimen (φ5 × 10 cm: n = 3) based on the description of JSCE F 506 and JSCE G 505, which are basically adopted in the mortar test, and in a sealed state. After standing at room temperature for 7 days, the uniaxial compressive fracture strength (qu) was measured and displayed in KN / m 2 units.

12.比表面積減少率
本試験は、乾燥対象素材の比表面積Aqならびに対象素材を固結成型した固結体の比表面積を自動BET比表面積測定装置[CARLOERABA社製Sorptomatic Series 1800]を用いて測定(m/g)し、対象素材に対する固結体の比表面積減少率(A)を下記式で求めた。

Figure 2006247645
軸圧縮強度(qh)を測定し、耐熱性強度保持率を下記q(%)で求めた。12 Specific surface area reduction rate In this test, the specific surface area Aq of the material to be dried and the specific surface area of the consolidated product obtained by consolidation molding of the target material were measured using an automatic BET specific surface area measuring device [Sorptomatic Series 1800 made by CARLOERABA] (m 2 / g), and the specific surface area reduction rate (A) of the solidified body relative to the target material was determined by the following formula.
Figure 2006247645
The axial compressive strength (qh) was measured, and the heat resistant strength retention was determined by the following q (%).

13.耐酸材料強度保持率
本試験は、予め調製した円柱状処理試験体(25℃)28日間養生の試験体一軸圧縮強度(q)を25℃でpH4の硝酸溶液中に1日間静置浸漬し、浸漬後の試験体一軸圧縮強度(qa)を測定し、下記式(q)の一軸圧縮強度の強度減少率が20%以内に保持されている場合を「耐酸性あり」と評価し、浸漬後処理試験体に異状が発生もしくは一軸圧縮強度の強度減少率が20%を超えている試験体を「耐酸性なし」と評価した。

Figure 2006247645
13. Acid-resistant material strength retention rate In this test, a preliminarily prepared cylindrically treated specimen (25 ° C.) for 28 days, the specimen uniaxial compressive strength (q 0 ) was allowed to stand still at 25 ° C. in a pH 4 nitric acid solution for 1 day. Measure the uniaxial compressive strength (qa) of the test specimen after immersion, and evaluate the case where the rate of decrease in the uniaxial compressive strength of the following formula (q) is maintained within 20% as “acid resistant”. A test specimen in which an abnormality occurred in the post-treatment specimen or the rate of decrease in the uniaxial compressive strength exceeded 20% was evaluated as “no acid resistance”.
Figure 2006247645

14.かさ密度の測定
供試料から切でした試験体片の長さ、幅、厚さを測定し、またその試験体の質量を測定し、下記数式(4)にて、かさ密度(P)を求めた。

Figure 2006247645
式中、Pはかさ密度(kg/m)を表し、mは試験体片の質量(kg)を表し、Vは試験体片の体積(m3)を表す。14 Measurement of bulk density Measure the length, width, and thickness of a specimen cut from the sample, measure the mass of the specimen, and obtain the bulk density (P) using the following equation (4). It was.
Figure 2006247645
In the formula, P represents the bulk density (kg / m 3 ), m represents the mass (kg) of the test piece, and V represents the volume (m3) of the test piece.

15.ダイオキシン類の簡易分析測定法
公定法としては、「特定管理一般廃棄物および特定管理産業廃棄物に係る規準の検定方法」(厚生省告示第192号、JISK0311:1999)にある高分解能GC/MS法、毒性等価係数:WHO−TEF(1998)に則るとあるが、本発明においては、試験体が多いことから「簡易分析測定法」によりダイオキシン類含有量を分析した。
15. Simplified analysis and measurement method for dioxins The official method is the high resolution GC / MS method in the “Testing method for criteria concerning specified controlled general waste and specified controlled industrial waste” (Ministry of Health and Welfare Notification No. 192, JISK0311: 1999). Toxicity equivalent coefficient: WHO-TEF (1998), but in the present invention, since there are many test specimens, the dioxins content was analyzed by the “simple analytical measurement method”.

「簡易分析測定法」は、供試料約10gを秤量し,1規定の塩酸に溶かして吸引ろ過する。ろ過後、残渣については、水分を除去するため、96ないしは168時間(4ないし7日間)粉関し、恒量とした後、ソックスレー抽出器で残渣中のダイオキシン類を還流抽出する。ろ液については,ろ液中のダイオキシンをトルエンやジクロロメタン名ふの有機溶媒で抽出する。In the “simple analytical measurement method”, about 10 g of a sample is weighed, dissolved in 1N hydrochloric acid and suction filtered. After filtration, in order to remove moisture, the residue is powdered for 96 to 168 hours (4 to 7 days), adjusted to a constant weight, and then dioxins in the residue are extracted by reflux with a Soxhlet extractor. The filtrate, to extract the dioxin in the filtrate in your organic solvent-toluene and dichloromethane name.

この有機溶媒で抽出した溶液と、先ほどソックスレー抽出器で還流抽出した溶液とを併せる。この併せた抽出液は,クリンアップ処理工程により大部分の狭雑物を硫酸処理にて除去し、極性物質を多層シリカゲルカラムにより、低極性物質をアルミナカラムにより、また活性炭埋蔵シリカゲルカラムを通して除去する。供雑物を除去した後、試料溶液を濃縮し、高分解能ガスクロマトグラフフ/高分解能質量分析計(GC/MS)で定量して、ダイオキシン類の含有量を測定分析した。  The solution extracted with the organic solvent is combined with the solution extracted by reflux with the Soxhlet extractor. In this combined extract, most of the impurities are removed by sulfuric acid treatment in the cleanup process, polar substances are removed by a multilayer silica gel column, low polar substances are removed by an alumina column, and activated carbon embedded silica gel column. . After removing contaminants, the sample solution was concentrated and quantified with a high resolution gas chromatograph / high resolution mass spectrometer (GC / MS) to measure and analyze the content of dioxins.

16.バリウム塩化合物のアルカリ溶液への可溶分測定方法
バリウムの「アルカリ溶液への可溶分」測定方法は、粉状バリウム塩化合物試料10gを25℃の1規定苛性ソーダ溶液100cc中に採り、10分間撹拌分散させた後、試料溶液を濾別して回収した溶液中のバリウムイオンを定量分析し、採取した試料中のバリウム元素全量を基準(100)とする1規定苛性ソーダ溶液1kg中に溶出したバリウムイオン(Ba++)量(mg/kg)を求めて算出した。
16. Method for Measuring Barium Salt Compound Soluble Content in Alkaline Solution Barium “soluble content in alkali solution” is measured by taking 10 g of a powdered barium salt compound sample in 100 cc of a 1N sodium hydroxide solution at 25 ° C. for 10 minutes. After stirring and dispersing, barium ions in the solution collected by separating the sample solution by filtration are quantitatively analyzed, and barium ions eluted in 1 kg of 1N sodium hydroxide solution based on the total amount of barium element in the collected sample (100) ( Ba ++ ) amount (mg / kg) was calculated and calculated.

13.リン酸分の徐放性
本発明の硬化補強組成物のリン酸化合物における「リン酸分の徐放性」は、供試料1gを25℃の4規定苛性ソーダ溶液100cc中に撹拌分散させる。次いで分散後の5分経過と120分経過にサンプリングし、分別濾過し、濾液中のリン酸分を五酸化リンとして定量(mg/100cc)し、グラフの横軸に経過時間(分)を、縦軸に五酸化リンの溶出積算量(mg/100cc)をプロットした直線の下記式(13)から初期リン酸分の溶出量bおよび平均加水分解速度定数aを算出した。
13. Sustained release property of phosphoric acid The “sustained release property of phosphoric acid content” in the phosphoric acid compound of the hardening reinforcing composition of the present invention is that 1 g of a sample is stirred and dispersed in 100 cc of a 4N sodium hydroxide solution at 25 ° C. Next, sampling was performed at 5 minutes and 120 minutes after dispersion, fractionated and filtered, the phosphoric acid content in the filtrate was quantified as phosphorus pentoxide (mg / 100 cc), and the elapsed time (minutes) was plotted on the horizontal axis of the graph. The amount of initial phosphoric acid eluted b and the average hydrolysis rate constant a were calculated from the following equation (13) in which the vertical axis represents the integrated amount of phosphorus pentoxide eluted (mg / 100 cc).

式13Equation 13

Y=aX+b(13)      Y = aX + b (13)

17.吸着体の脱臭効果の試験方法
17−1 代表的悪臭に対する脱臭効果(官能評価)
評価方法は、1.8リッターのガラス瓶に臭気濃度が官能評価で3になるように所定量の各悪臭成分(アンモニア、トリメチルアミン、硫化水素、E−メルカプタン、硫化メチル、イソ吉草酸、酢酸)を入れ、ついで供試料の吸着体1gを加えて常温に6時間放置した後、瓶中の気体0.1リッターを取り出し、次に示す4段階の官能評価基準にしたがって評価した。
17. Test method for deodorizing effect of adsorbent 17-1 Deodorizing effect on typical malodor (sensory evaluation)
The evaluation method is to add a predetermined amount of each malodorous component (ammonia, trimethylamine, hydrogen sulfide, E-mercaptan, methyl sulfide, isovaleric acid, acetic acid) so that the odor concentration is 3 in the sensory evaluation in a 1.8 liter glass bottle. Then, 1 g of the adsorbent of the sample was added and allowed to stand at room temperature for 6 hours. Then, 0.1 liter of gas in the bottle was taken out and evaluated according to the following four sensory evaluation criteria.

17−2 各種悪臭に対する静的脱臭容量評価方法は、0.1リッターのガラス瓶に、濃度(mg/リッター)を変量させた所定量の悪臭成分(アンモニア、トリメチルアミン、硫化水素)を入れ、ついで供試料の吸着体1gを加えて常温で24時間放置する。24時放置された供試料において悪臭成分が検出されない悪臭成分の最大濃度点を静的脱臭容量として評価した。  17-2 Static deodorizing capacity evaluation method for various bad odors is as follows. A predetermined amount of malodorous components (ammonia, trimethylamine, hydrogen sulfide) with varying concentrations (mg / liter) are placed in a 0.1 liter glass bottle, and then supplied. Add 1 g of sample adsorbent and leave at room temperature for 24 hours. The maximum concentration point of malodorous components in which malodorous components were not detected in the samples left at 24 hours was evaluated as the static deodorizing capacity.

17−3 各種悪臭に対する動的脱臭容量評価方法は、まず内径15mmのガラス製カラムに5cmの長さになるように供試料の吸着体を詰める。次いで、約1%濃度に調製したガス状の悪臭成分(アンモニア、トリメチルアミン、硫化水素)を200ml/分の速度でカラム中の供試料吸着体中を通過せしめる。この操作で悪臭成分が供試料吸着体に吸着されずに出てくる通過量から動的脱臭容量を測定して評価した。  17-3 In the dynamic deodorizing capacity evaluation method for various bad odors, first, a sample adsorbent is packed into a glass column having an inner diameter of 15 mm so as to have a length of 5 cm. Next, gaseous malodorous components (ammonia, trimethylamine, hydrogen sulfide) prepared to a concentration of about 1% are allowed to pass through the sample adsorbent in the column at a rate of 200 ml / min. The dynamic deodorizing capacity was measured and evaluated from the passing amount of the malodorous component that was not adsorbed by the sample adsorbent by this operation.

本実施例において、有害物質を共存する熱履歴シリケートからなる改質処理素材に改質処理剤、必要に応じて機能付与剤を配合して、水系溶媒を介する一連の作業工程(準備工程、調整工程、加工工程、養生工程)に付する改質方法により、該改質処理素材に無害化処理および形状化処理が施されて、趣向資材、生活資材、工業用資材、建材、土木資材、自然環境資材ないし緑化・造園資材等として供給される原位置非成型品、耐水性粉粒体品、形状加工成型品、活性粉体結着品、基材積層複合品、顆粒群体集合品ないしは注充填一体化品からなる耐水性の結着形状体について、参考例を添えた具体的例示を以って以下に説明する。  In this example, a reforming treatment material composed of a heat history silicate coexisting with harmful substances is blended with a reforming treatment agent and, if necessary, a function-imparting agent. Process, processing process, and curing process), the modified material is detoxified and shaped, and is used as a preference material, living material, industrial material, building material, civil engineering material, nature In-situ non-molded products supplied as environmental materials or greening / landscaping materials, water-resistant granular products, shape-processed molded products, active powder binders, base laminate composites, granule aggregates, or injection filling The water-resistant binder-shaped body made of an integrated product will be described below with specific examples with reference examples.

[参考例1]改質処理素材
本参考例において、本実施例で採択される有害物質を共存する熱履歴シリケートからなる改質処理素材を下記処理方法により調製された表6に示す人工合成品を選び、また廃棄物類としては、表7に示す廃棄物類から選んだ。
[Reference Example 1] Modified Treatment Material In this reference example, an artificial synthetic product shown in Table 6 prepared by the following treatment method was used as a modified treatment material comprising a heat history silicate coexisting with harmful substances adopted in the present example. The wastes were selected from the wastes shown in Table 7.

人工合成品からなるシリケートは、下記表3,4,5に示すシリケート組成物、カルシヤ組成物、アルミナ組成物より選択し、表6に示す量割合の混合原料と温度で処理した処理品を粉砕・分級して100メッシュ篩通過シリケートを人工合成品とした。  The silicate made of an artificially synthesized product is selected from the silicate composition, the calcite composition, and the alumina composition shown in Tables 3, 4 and 5 below, and the processed product treated with the mixed raw material and the temperature in the amount ratio shown in Table 6 is pulverized.・ Classification and 100-mesh sieve silicate was used as an artificial synthetic product.

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[参考例2]改質処理剤用の材料
本参考例において、本実施例の改質処理剤の配合原料として採択したナトリウム含有成分、カルシヤ含有成分ならびに硫黄含有成分を市販試薬、工業薬品、試作品等より採択して表8に示す。

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[Reference Example 2] Material for modifying agent In this reference example, sodium-containing component, calcium-containing component and sulfur-containing component which were adopted as the raw materials for the modifying agent of the present example were used as commercially available reagents, industrial chemicals, Selected from works, etc. are shown in Table 8.
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[参考例3]改質処理剤
本参考例において、本実施例で採択する改質処理剤として、市販試薬、工業薬品、試作品より表9に示すそれぞれの有効成分を含有するナトリウム含有成分、カルシヤ含有成分ならびに硫黄含有成分の組成内容と有姿による数量配合割合、さらにpH値を表9に併せ表示した。
[Reference Example 3] Modification Treatment Agent In this reference example, as a modification treatment agent adopted in this example, commercially available reagents, industrial chemicals, sodium-containing components containing each active ingredient shown in Table 9 from a prototype, Table 9 shows the composition content of the calcium-containing component and the sulfur-containing component, the quantity blending ratio depending on the appearance, and the pH value.

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[参考例4]比較例
本参考例では、本発明における改質処理剤の作用効果を比較評価ために本発明改質処理剤の比較例成分の4種類を選び表10に示した。

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[Reference Example 4] Comparative Example In this reference example, four types of comparative example components of the modified treatment agent of the present invention were selected and shown in Table 10 in order to compare and evaluate the effects of the modified treatment agent of the present invention.
Figure 2006247645

[参考例5]サプリメント
本参考例において、本実施例で採択する機能付与剤であるサプリメントとして、市販試薬、工業薬品、廃棄物類の精製品ならびに予め精製・調製した材料類の中から、硫化ナトリウムであるアルカリ補充組成物、酸化鉄、硫化鉄、ボーキサイトである鉄塩補充組成物、さらにフェロケイ酸塩である酸性白土、タルクおよびベントナイト、さらにシラノール基を有するケイ酸ソーダであるケイ酸塩補充組成物をそれぞれ選び、主たる化学組成とともに表11に示す。
[Reference Example 5] Supplement In this reference example, as a supplement which is a function-imparting agent adopted in the present example, a sulfurized sulfite is selected from commercially available reagents, industrial chemicals, purified products of wastes, and previously purified and prepared materials. Alkaline supplement composition that is sodium, iron oxide, iron sulfide, iron salt supplement composition that is bauxite, acid clay, talc and bentonite that are ferrosilicates, and silicate supplement that is sodium silicate with silanol groups Each composition was selected and shown in Table 11 along with the main chemical composition.

なお、アルカリ補充組成物である炭カル変性組成物には貝殻変性組成物を選んだ。貝殻変性組成物は、廃棄処分されているホタテの貝殻粉末(主成分:カルシヤ54.3質量%)100質量部に対して、油脂類の精製に使用した活性白土で油分を含んでいる廃白土60質量部の二者による混合物をそれぞれ約1000℃で熱処理し、次いで熱活用品を粉砕・分級して貝殻変性組成物とした。  A shell-modified composition was selected as the charcoal-modified composition, which is an alkali supplement composition. The shellfish modified composition is waste white clay containing oil in the activated white clay used for refining fats and oils with respect to 100 parts by weight of scallop shell powder (main component: Calcia 54.3% by mass) that has been disposed of. 60 parts by mass of the mixture of the two were each heat-treated at about 1000 ° C., and then the heat-utilized product was pulverized and classified to obtain a shell-modified composition.

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[参考例6]インプルーブメント
本参考例において、本実施例で採択する機能付与剤であるインプルーブメントとして、市販試薬、工業薬品、廃棄物類の精製品等の中から、原子力発電所において、低レベル廃棄物を減容固化処理するときのケイ酸アルカリ系固化材の硬化剤として採択されているリン酸ケイ素[シリカ/5酸化リンモル比が3.0:1.0で950℃焼成した粉砕品]を選んだ。
[Reference Example 6] Improvement In this reference example, the improvement, which is a function-imparting agent adopted in the present example, is a low-priced value in a nuclear power plant among commercially available reagents, industrial chemicals, and refined waste products. Silicon phosphate [silica / phosphorus pentoxide molar ratio of 3.0: 1.0 and pulverized product baked at 950 ° C. as a curing agent for alkali silicate-based solidifying material for volume reduction solidification treatment of level waste ] Was selected.

さらに自動車用鋼板を処理した際に副生する主成分が質量%でリン酸鉄25.0、リン酸亜鉛7.5.シリカ10.5、アルミナ8.4、水分35.0のリン酸塩スラッジ、また水ガラスの硬化剤であるリン酸アルミニウム粉末、さらにまた輸入鉱石のりん鉱石、さらに工業薬品のリン酸鉄からなるリン酸根組成物を選んだ。  Furthermore, the main components by-produced when the steel plate for automobiles is processed are mass%, and iron phosphate 25.0, zinc phosphate 7.5. It consists of phosphate sludge with silica 10.5, alumina 8.4, moisture 35.0, water glass hardener, aluminum phosphate powder, imported ore, and industrial chemical iron phosphate. A phosphate radical composition was chosen.

また、本実施例で採択する機能付加成分であるインプリメントとして、本発明改質処理剤と水系溶媒との反応速度を遅延させて作業性を確保する遅延剤として、簡易反応型で調製したケイ酸バリウム(酸化バリウム/シリカモル比=1.0:1.0、250℃で反応・粉砕品)と市販工業薬品の水酸化バリウムからなるバリウム塩組成物を選んだ。  In addition, as an implementation as a functional addition component adopted in this example, silicic acid prepared in a simple reaction type as a retarder that delays the reaction rate between the present modification treatment agent and an aqueous solvent to ensure workability. A barium salt composition consisting of barium (barium oxide / silica molar ratio = 1.0: 1.0, reaction and pulverized product at 250 ° C.) and commercial industrial chemical barium hydroxide was selected.

さらにまた、本実施例で採択する機能付加成分であるインプリメントとして、市販の工業薬品よりホワイトカーボン、カオリン、フライアッシュ、高炉スラグならびにホタテ貝殻の粉末からなる分散媒質組成物を選んだ。
以上のインプルーブメントを表12に表示した。
Furthermore, a dispersion medium composition composed of white carbon, kaolin, fly ash, blast furnace slag and scallop shell powder was selected from commercially available industrial chemicals as an implement as a functional addition component adopted in this example.
The above improvements are shown in Table 12.

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[参考例7]ファンクションメント
本参考例において、本実施例で採択する機能付与剤であるファンクションメントとして、市販試薬、工業薬品、廃棄物類の精製品等の中から、繊維状体、フレーク状体および砂状体等を含む粉粒体で必要に応じて精製された材料から、結晶タネ組成物、緩衝帯形成組成物、担持吸着組成物、耐熱火組成物、断熱・保温組成物、沈殿凝集組成物もしくは機能付与組成物を選び表13に示す。
[Reference Example 7] Functionment In this reference example, as a functionment which is a function-imparting agent adopted in the present example, a commercial product, an industrial chemical, a refined product such as waste, a fibrous material, a flaky shape, etc. Crystal seed composition, buffer band forming composition, supported adsorption composition, heat-resistant fire composition, heat insulation / heat-retaining composition, precipitation from materials refined as necessary with powder and granular materials including sand and sand The aggregate composition or function-imparting composition is selected and shown in Table 13.

結晶タネ組成物としては、アルミノケイ酸塩でAl/Si原子比が4.2で、環員数8で2次粒径20μ以下の4A型合成ゼオライト、福島産天然ゼオライトから選んだ。
緩衝帯形成組成物としては、ホウ酸、ホウ酸ナトリウムならびにホウ酸アルミニウムから選んだ。
The crystal seed composition was selected from a 4A-type synthetic zeolite having an Al / Si atomic ratio of 4.2, a ring member number of 8 and a secondary particle size of 20 μm or less, and a natural zeolite from Fukushima.
The buffer zone forming composition was selected from boric acid, sodium borate and aluminum borate.

担持吸着組成物としては、産廃であるペーパースラッジを乾留して炭素化した炭−ケイ酸アルミニウム複合物(主成分%:炭素::25.5、シリカ:35.6、アルミナ27.5、カルシヤ12.4)ならびに活性炭、シリカゲル、アルミナゲルから選んだ。
耐熱火組成物としては、マグネシヤ、アルミナ、炭化ケイ素、ケイ酸カルシウム、ケイ酸アルミニウムから選んだ。
As the supported adsorption composition, a carbon-aluminum silicate composite obtained by carbonizing paper sludge as industrial waste (main component%: carbon :: 25.5, silica: 35.6, alumina 27.5, calcium oxide) 12.4) as well as activated carbon, silica gel and alumina gel.
The heat-resistant fire composition was selected from magnesium, alumina, silicon carbide, calcium silicate, and aluminum silicate.

断熱・保温組成物としては、かさ比重が0.1ないしは1.0g/ccであり、また650℃における熱収縮率が2.0%以下のゾーノトライトならびにトバモライトであるケイ酸カルシウムを選んだ。  As the heat insulating and heat retaining composition, zonotolite having a bulk specific gravity of 0.1 to 1.0 g / cc and a heat shrinkage at 650 ° C. of 2.0% or less and calcium silicate as tobermorite were selected.

沈殿凝集組成物としては、前記のシリケートの混合原料を構成するカルシヤ組成物であり、表4に示したカルシヤを少なくとも20質量%以上含有するカルシウム塩組成物、廃棄物類組成物、カルシヤ含有鉱物組成物もしくは炭カル変性組成物の群より選ばれる単独ないし2種以上の組み合わせカルシウム塩化合物を主成分とする組成物であり、必要に応じてカルシヤ含有組成物100質量部に対して、食塩を3ないし20質量部配合されており粒径が1000μ以下である粉粒体のカルシヤ含有組成物を選んだ。  The precipitated agglomeration composition is a calcite composition constituting the silicate mixed raw material, and includes a calcium salt composition containing at least 20% by mass or more of the calcite shown in Table 4, a waste composition, and a calcite-containing mineral. It is a composition comprising as a main component a single or two or more combined calcium salt compounds selected from the group of compositions or charcoal cal-modified compositions, and salt is added to 100 parts by mass of the calcia-containing composition as necessary. A granular-containing composition containing 3 to 20 parts by mass and having a particle size of 1000 μm or less was selected.

機能付与組成物としては、塗料ならびにプラスチクス業界等で汎用されている顔料、着色剤、活性剤、充填剤、磁石と磁性体、触媒、酸化性化合物、無機質系の硫酸アルミニウム、アオコ沈殿剤からなる凝集分離剤、殺虫剤、殺菌剤、合成肥料、栄養剤等からなる農薬・除草剤・肥料・微生物活性栄養剤、消臭剤、植物の種子や菌類、抗菌剤、ホウ酸亜鉛、ホウ酸銀からなる抗微生物剤、活性炭粉末にジメチルジメトキシシランを10質量%含浸させた撥水剤および各種の機能付加剤から選んだ。  The function-imparting composition is composed of pigments, colorants, activators, fillers, magnets and magnetic materials, catalysts, oxidizing compounds, inorganic aluminum sulfate, and ako precipitants commonly used in the paint and plastics industries. Pesticides, herbicides, fertilizers, microbial active nutrients, deodorants, plant seeds and fungi, antibacterial agents, zinc borate, silver borate Selected from the group consisting of an antimicrobial agent, a water repellent obtained by impregnating 10% by mass of dimethyldimethoxysilane into activated carbon powder, and various functional additives.

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[参考例8]機能付与剤であるレインホースメント
本参考例において、本実施例で採択する機能付与剤であるレインホースメントとして、市販試薬、工業薬品、廃棄物類の精製品等の中から、粗骨材である一般土木分野等で採択されている粒径が5ないし12mmφの砂利・砕石、細骨材である川砂、比重の軽いパーライト、また比重の大きい鉄鉱石、さらに焼却灰の溶融スラグやガラスカレット、繊維質組成物は、無機質製品やプラッスチックス製品における加工業界で採用されている長い方で5mm未満であるステンレス製繊維、ガラス繊維、炭素繊維、植物性(パルプ状)繊維を選び主たる成分を表14に示す。
[Reference Example 8] Rain reinforcement as a function-imparting agent In this reference example, as a rain reinforcement as a function-imparting agent adopted in this example, among commercially available reagents, industrial chemicals, and refined products of wastes, etc. , Gravel and crushed stone with a particle size of 5-12mmφ adopted in the field of general civil engineering as coarse aggregate, river sand as fine aggregate, light pearlite with specific gravity, iron ore with high specific gravity, and melting of incineration ash Slag, glass cullet, and fiber composition are made of stainless steel fibers, glass fibers, carbon fibers, and vegetable (pulp-like) fibers that are less than 5 mm long and are used in the processing industry for inorganic and plastic products. Table 14 shows the main components selected.

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[参考例9]
本参考例では、下記表15に示す廃棄物類の中から水吸収性に富む熱履歴シリケートと同じく廃棄物類であるが含水状態にある汚泥・底質等を組み合わせたて含水量の調整された混合廃棄物類を挙げる。
[Reference Example 9]
In this reference example, the water content is adjusted by combining sludge and sediments, etc., which are the same as the heat-history silicate, which is rich in water absorption, but are in the water-containing state, among the wastes shown in Table 15 below. List the mixed waste.

本実施例で採択した混合廃棄物類は、乾燥物状態の廃棄物類(生ゴミ焼却灰、下水汚泥灰、高炉スラグ,ペパースラジ灰等)100質量部に対して、含水状態にあり、少なくとも固形分を25質量%以上含有する廃棄物類(海域底質ケーキ、湖沼底質ケーキ、浄水処理ケーキ、下水汚泥ケーキ、農業集落汚泥ケーキ等)により混合廃棄物類とした。  The mixed wastes adopted in this example are in a water-containing state with respect to 100 parts by mass of wastes in a dry state (eg, garbage incineration ash, sewage sludge ash, blast furnace slag, pepper sludge ash, etc.), and at least solid Wastes containing 25% by mass or more of waste (sea bottom sediment cake, lake bottom sediment cake, water purification cake, sewage sludge cake, agricultural settlement sludge cake, etc.) were used as mixed waste.

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[実施例1]代表例+比較例
本実施例において、熱履歴シリケートを改質処理素材として改質処理剤を活用する一連の作業工程に付する改質処理方法、ならびに改質処理素材に改質処理方法による無害化処理ならびに形状化処理が施された構造体からなる接着形状体の代表的な実施例について説明する。なお、本実施例においては、本発明技術の比較例と代表的な従来技術による比較例を添えて説明する。
[Example 1] Representative example + comparative example In this example, the heat treatment silicate is used as a reforming treatment material, and the reforming method is applied to a series of work steps utilizing a reforming treatment agent. A typical embodiment of an adhesive shape body composed of a structure subjected to a detoxification process and a shape process by a quality treatment method will be described. In this embodiment, a comparative example of the technique of the present invention and a comparative example of a typical prior art will be described.

改質処理素材として熱履歴シリケートを参考例1に示した中から選び、改質処理剤をは参考例3に示した中から選び、水系溶媒として水道水を選び表16に示した。以上の種類と配合内容、さらに活性化混和物の調製条件、調製された混和物のpH値、さらに養生条件を表16に併せ表示した。
なお、以下本実施例における改質処理剤の配合数量は請求項で示す有効成分換算量でなく有姿量で示した。試験用供試体は、下記に示す試験仕様に従って調製した。
The heat history silicate was selected from those shown in Reference Example 1 as the reforming material, the reforming agent was selected from those shown in Reference Example 3, and tap water was selected as the aqueous solvent and shown in Table 16. The above types and contents of blending, the preparation conditions of the activated admixture, the pH value of the prepared admixture, and the curing conditions are also shown in Table 16.
In addition, the compounding quantity of the modification | reformation processing agent in a present Example was shown not by the effective component conversion amount shown by the claim but by the solid amount below. Test specimens were prepared according to the test specifications shown below.

本実施例における構造体からなる試験用供試体の調整は、選んだ材料1Kgをセメントモルタルの試験調製に使用されるセメントモルタル試験用ミキサーに採り、約10分間撹拌混和・混練して可塑状ないしはモルタル状の活性化混和物に調製した。加工工程は、調製した活性化混和物を[物性評価試験方法]項記載に則り、プラスチック製モールド型(φ50×100mmの円柱状)に充填し、次いで上部をフイルムでシール密封して円柱状試験体用に成型加工した。養生工程は、所定の養生条件で養生し、養生後試験体を脱型した構造体をそれぞれの試験用供試体とした。
なお、本明細書における各実施例における試験用供試体の調製は、特記しない限り、以降の試験用供試体調製も基本的に本実施例で記載の試験仕様と同様にして行った。
Preparation of the test specimen composed of the structure in this example is carried out by taking 1 Kg of the selected material into a cement mortar test mixer used for preparing a test for cement mortar, stirring and mixing and kneading for about 10 minutes to form a plastic material or Prepared in a mortar activated blend. In the processing step, the prepared activated admixture is filled into a plastic mold (cylindrical shape of φ50 × 100 mm) in accordance with the description in [Method for evaluating physical properties], and then the upper part is sealed and sealed with a film. Molded for body use. In the curing process, a structure obtained by curing under predetermined curing conditions and demolding the specimen after curing was used as each test specimen.
The test specimens in each example in this specification were prepared in the same manner as the test specifications described in this example, unless otherwise specified.

また、本発明技術の比較例として、本発明改質処理剤に対比して、参考例4で示した比較例成分4種類(比較例試料番号H−01〜04)を選んだ。次いで、従来技術の汎用常温固化材であるポルトランドセメント(JIS R 5210、試料番号:H−5)ならびに汎用水ガラス系固化材である2号水ガラスに硬化剤リン酸アルミニウムを加えた水ガラス組成物(試料番号:H−6)を選んだ。  In addition, as a comparative example of the technology of the present invention, four types of comparative example components (comparative sample numbers H-01 to 04) shown in Reference Example 4 were selected in comparison with the modified treatment agent of the present invention. Subsequently, Portland cement (JIS R 5210, sample number: H-5), which is a conventional general-purpose solidifying material, and water glass composition in which a hardener aluminum phosphate is added to No. 2 water glass, which is a general-purpose water glass-based solidifying material. (Sample number: H-6) was selected.

また、従来技術である本発明者先願特許技術で対比される比較例として、特開平11−263661記載の試料番号C−1に準拠して試作したシリカ系バインダー(試料番号:H−7)、特開2002−128550記載の試料番号1−1に準拠して試作したアルカリ系硬化剤[主成分:カルシヤ+粘土+苛性ソーダ、試料番号:H−8]さらに特願2003−363842記載の試料番号1−1に準拠して試作したシラノール基含有処理材[主成分:シリケートガラス+アクティブシリカ+サルフェイト、試料番号:H−9]を選び、それぞれの比較例を表16に併せ表示した。  In addition, as a comparative example compared with the prior art technology of the present inventor's prior application, a silica-based binder (sample number: H-7) prototyped according to sample number C-1 described in JP-A-11-263661. , Alkali-based curing agent prototyped according to Sample No. 1-1 described in JP-A No. 2002-128550 [Main component: Calcia + Clay + Caustic soda, Sample No .: H-8] and Sample No. described in Japanese Patent Application No. 2003-363842 The silanol group-containing treatment material [main component: silicate glass + active silica + sulfate, sample number: H-9] prepared in accordance with 1-1 was selected and each comparative example was also displayed in Table 16.

以上のそれぞれ各条件で調製された試験用供試体を[物性評価試験方法]項記載の試験方法により、それぞれ供試体の物性[水溶出pH、耐水性、耐熱性、有害元素群の溶出等]を試験評価した。なお、本実施例における有害元素群の溶出試験は、対象とする有害元素は、砒素、セレン、ホウ素、フッ素の4元素を代表して選び、中性域と酸性域の2条件下での溶出を評価した。なお、本実施例で改質処理素材とした無処理フライアッシュにおける有害元素群の溶出試験も比較のために行い表示した。
以上の結果を表17に併せ表示した。
The test specimens prepared under the respective conditions described above were tested according to the test methods described in the section [Physical property evaluation test method], and the physical properties of each specimen [water elution pH, water resistance, heat resistance, elution of harmful element group, etc.] The test was evaluated. In addition, in the elution test of the harmful element group in this example, the target harmful elements are selected from four elements of arsenic, selenium, boron, and fluorine, and the elution is performed under two conditions of neutral and acidic ranges. Evaluated. In addition, the elution test of the harmful element group in the non-processed fly ash used as the modified material in this example was also displayed for comparison.
The above results are also shown in Table 17.

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以上の結果、本発明改質方法の条件範囲にしたがって、それぞれ調製した本実施例の接着形状体は、いずれも水溶出pH値が10未満を示し、耐水性で耐熱性に形状化処理が施されており、しかも中性域のみならず酸性域においても溶出有害元素群は固定・不溶化状態(参考とする環境基準値:表1参照)に無害化処理が施されていることが良く理解される。  As a result of the above, according to the condition range of the modification method of the present invention, each of the adhesive shaped bodies prepared in this example has a water elution pH value of less than 10, and is water-resistant and heat-resistant. In addition, it is well understood that the toxic element group that has been dissolved in the neutral as well as the neutral range has been subjected to the detoxification treatment in the fixed and insolubilized state (reference environmental standards: see Table 1). The

一方、比較例においては、本発明改質処理剤の必須要件を満足しない比較成分では、いずれも本発明の目的、例えば耐水性等が得られず、また特に酸性域での有害元素の溶出を阻止することはできず、本発明改質処理剤の優位性が良く理解できる。さらに、既存の処理固化材であるポルトランドセメントでは、耐熱性は得られず、水ガラス系固化材では耐水性は得られず、いずれもpH値は高く、中性域での有害元素の溶出を阻止することはできなかった。さらに、本発明者等の先願特許技術で対比される比較例では、フッ素およびホウ素の溶出を阻止することはできなかった。特に試料番号H−08では配合されているアルカリ成分からなる硬化剤の配合量が本発明よりも多いこともあり、有害元素の充分なる溶出を阻止することはできなかった。  On the other hand, in comparative examples, the comparative components that do not satisfy the essential requirements of the present modification treatment agent do not provide the object of the present invention, for example, water resistance, etc., and elution of harmful elements particularly in the acidic range. It cannot be blocked, and the superiority of the present modification treatment agent can be well understood. In addition, Portland cement, which is an existing treatment solidified material, does not provide heat resistance, and water glass-based solidified material does not provide water resistance, both of which have a high pH value and elution of harmful elements in the neutral range. I couldn't stop. Furthermore, in the comparative example compared with the prior patent technology of the present inventors, elution of fluorine and boron could not be prevented. In particular, in Sample No. H-08, the blending amount of the curing agent composed of the alkali component blended was larger than that of the present invention, and sufficient elution of harmful elements could not be prevented.

[実施例2]各種改質対象素材+各種改質処理剤
本実施例において、本発明の代表的な熱履歴シリケートを改質処理素材として、代表的な改質処理剤を採択して一連の作業工程に付する改質方法により、改質処理素材に無害化処理ならびに形状化処理が施される構造体からなる結着形状体について説明する。
[Example 2] Various reforming target materials + various reforming treatment agents In this example, a representative heat treatment silicate of the present invention is used as a reforming treatment material, and a series of reforming treatment agents are adopted. A binding shape body composed of a structure in which a modification treatment material is subjected to a detoxification process and a shaping process by a modification method applied to a work process will be described.

改質処理素材として熱履歴シリケートであるペパースラジ灰(TSW03)を選び、改質処理剤を参考例3に示した中から選び、水は水道水を選び表18に示した。以上の種類と配合内容、活性化混和物の調製条件、調製混和物のpH値、養生条件を表18に併せ表示した。試験用供試体は、実施例1記載の試験仕様に従い調製した。  Pepper sludge ash (TSW03), which is a heat history silicate, was selected as the reforming material, the reforming agent was selected from those shown in Reference Example 3, and tap water was selected as the water shown in Table 18. The above types and blending contents, the preparation conditions of the activated blend, the pH value of the prepared blend, and the curing conditions are also shown in Table 18. Test specimens were prepared according to the test specifications described in Example 1.

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以上調製した各混和物を[物性評価試験方法]項記載に則り、それぞれ物性[水溶出pH、耐水性、耐熱性、中性域と酸性域における鉛溶出等]を試験評価し、無処理ペパースラジ灰の4元素の溶出試験結果を含めてその結果を表19に併せ表示した。  Each of the prepared blends was tested and evaluated for the physical properties [water elution pH, water resistance, heat resistance, lead elution, etc. in neutral and acidic range] in accordance with the description in [Method for evaluating physical properties], and untreated pepper sludge The results including the dissolution test results for the four elements of ash are also shown in Table 19.

以上の結果、本発明改質処理法により、各種の改質処理素材に対して、各種の改質処理剤を採択して調製した活性化混和物を経由した各接着形状体は、水溶出pH値が10未満を示し、耐水性で耐熱性に形状化処理が施され、しかも中性域のみならず酸性域においても溶出有害元素群は固定・不溶化状態に無害化処理が施されており、無公害型接着形状体として有効であることが良く理解される。  As a result of the above, according to the modification treatment method of the present invention, each adhesive shaped body via the activated admixture prepared by adopting various modification treatment agents for various modification treatment materials has a water-elution pH. The value is less than 10, the water-resistant and heat-resistant shaping treatment is applied, and the eluting harmful element group is fixed and insolubilized in a neutralized as well as an acidic region, It is well understood that it is effective as a pollution-free bonded shape.

[実施例3]水系溶媒各種 多段の代表例
本実施例において、海域底質(ヘドロ)からなる熱履歴シリケートを改質処理素材として、各種の改質処理剤を採択し、各種の水系溶媒により混和物として、ついで多段式曝露を含む養生条件の下で一連の作業工程に付する改質方法により、改質処理素材に無害化処理ならびに形状化処理が施された構造体からなる接着形状体について説明する。
[Example 3] Various types of aqueous solvents Representative examples of multiple stages In this example, various reforming treatment agents were adopted using heat history silicate composed of marine sediment (sludge) as a reforming treatment material, and various aqueous solvents were used. As an admixture, an adhesive shape consisting of a structure in which the modified material is detoxified and shaped by a modification method that is subjected to a series of work steps under curing conditions including multistage exposure. Will be described.

改質処理素材として海域底質ケーキ(TSW10)を選び、改質処理剤を参考例3に示した中から選び、さらに必要に応じて機能付与剤を参考例8に示したレインホースメント中から選び、選んだ水系溶媒は表20に示した。表20に示した配合内容で常温×10分間混和し、調整された活性化混和物のpH値、さらに養生条件を表20に併せ表示した。試験用供試体は、実施例1に示した試験仕様にしたがって調製した。  Select the marine sediment cake (TSW10) as the reforming treatment material, select the reforming treatment agent from those shown in Reference Example 3, and further select the function-imparting agent from the rain reinforcement shown in Reference Example 8 as necessary. The selected aqueous solvents are shown in Table 20. The mixture content shown in Table 20 was mixed at room temperature for 10 minutes, and the pH value of the adjusted activated mixture and the curing conditions were also displayed in Table 20. Test specimens were prepared according to the test specifications shown in Example 1.

調製した各円柱状の試験供試体における物性[水溶出pH、耐水性、耐熱性、一軸圧縮強度(q=KN/m)、鉛の中性域ならびに酸性域の溶出試験]を物性評価試験方法の項で示した試験方法に則りそれぞれ測定してそれぞれを評価した。
それらの結果を表21に併せ表示した。
Physical property evaluation test of physical properties [elution test of water elution pH, water resistance, heat resistance, uniaxial compressive strength (q = KN / m 2 ), lead neutral and acidic range] in each prepared cylindrical test specimen Each was measured according to the test method shown in the method section and evaluated.
The results are also shown in Table 21.

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以上の結果、本発明改質処理法により、改質処理剤に機能付与剤を加え、さらに各種の水系溶媒により調製した混和物を経由し、養生条件も単式ならびに多段式養生条件下、特に水中養生にて調製した各接着形状体においても、水溶出pH値が10未満を示し、耐水性で耐熱性に形状化処理が施され、鉛で代表する溶出試験で中性域のみならず酸性域においても良好な固定・不溶化状態が確認される無害化処理が施されており、無公害型接着形状体として有効であることが良く理解される。  As a result of the above, according to the modification treatment method of the present invention, a function-imparting agent is added to the modification treatment agent, and further, through the blends prepared with various aqueous solvents, the curing conditions are single and multi-stage curing conditions, particularly underwater. Each adhesive shape body prepared by curing also has a water elution pH value of less than 10, is shaped to be water-resistant and heat-resistant, and is an acidic region as well as a neutral region in lead elution tests. It is well understood that a detoxification treatment for confirming a good fixed / insolubilized state is performed, and it is effective as a pollution-free adhesive shape.

[実施例4]改質処理剤+機能付与剤=複合改質処理剤
本実施例において、石炭灰(TSW02)と高炉スラグ(TSW07)の2者混合廃棄物を改質処理素材として、改質処理剤と機能付与剤で構成されてワンパック化された複合改質処理剤を採択して一連の作業工程に付する改質方法により、混合廃棄物に無害化処理ならびに形状化処理が施された構造体からなる接着形状体について説明する。
[Example 4] Reforming treatment agent + function imparting agent = composite reforming treatment agent In this example, two-component mixed waste of coal ash (TSW02) and blast furnace slag (TSW07) is used as a reforming treatment material. The mixed waste is detoxified and shaped by a reforming method that adopts a one-pack composite reforming treatment agent composed of a treatment agent and a function-imparting agent and applies it to a series of work steps. The bonded shape body made of the structure will be described.

改質処理素材として混合廃棄物である石炭灰(TSW02)100質量部と高炉スラグ(TSW07)100質量部の等量混合廃棄物(TSW14)を選んだ。改質処理剤を参考例2に示した中から選び、機能付与剤は参考例5ないし8に示した中から選び、水系溶媒は水道水を選んだ。以上の種類と配合内容と活性化混和物のpH値を表22に併せ表示した。この時該混和物は常温×10分間で調製し、養生条件は全て常温×28日で行い、試験用供試体は、実施例1に示した試験仕様に従って調製した。  As a reforming treatment material, an equivalent mixed waste (TSW14) of 100 parts by mass of coal ash (TSW02) and 100 parts by mass of blast furnace slag (TSW07), which is a mixed waste, was selected. The modifying agent was selected from those shown in Reference Example 2, the function-imparting agent was selected from those shown in Reference Examples 5 to 8, and tap water was selected as the aqueous solvent. The above types, blending contents, and pH value of the activated admixture are shown together in Table 22. At this time, the admixture was prepared at room temperature × 10 minutes, all curing conditions were performed at room temperature × 28 days, and the test specimens were prepared according to the test specifications shown in Example 1.

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調製した各円柱状の試験供試体における物性[水溶出pH、耐水性、耐熱性、一軸圧縮強度(q=KN/m)、ホウ素の中性域および酸性域の溶出試験]を物性評価試験方法の項で示した試験方法に則り評価した。それらの結果を表23に併せ表示した。Physical property evaluation test of physical properties [elution test of water elution pH, water resistance, heat resistance, uniaxial compressive strength (q = KN / m 2 ), boron neutral and acidic range] in each prepared cylindrical test specimen Evaluation was performed according to the test method shown in the method section. The results are also shown in Table 23.

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以上の結果、本発明改質処理法により、石炭灰と高炉スラグの2者混合廃棄物を改質処理素材として、改質処理剤に各種の機能付与剤を併配合した混和物を経由して調製した各接着形状体は、水溶出pH値が10未満を示し、耐水性で耐熱性に形状化処理が施され、鉛で代表する溶出試験で中性域のみならず酸性域においても良好な固定・不溶化状態が確認される無害化処理が施されていることが良く理解される。  As a result of the above, the modified treatment method of the present invention uses a mixed waste of coal ash and blast furnace slag as a modified treatment material, and via a mixture in which various functionalizing agents are blended with the modified treatment agent. Each prepared adhesive body has a water elution pH value of less than 10, and is shaped to be water-resistant and heat-resistant, and is good not only in the neutral region but also in the acidic region in a lead dissolution test represented by lead. It is well understood that a detoxification process for confirming the fixed / insolubilized state is performed.

[実施例5]含水複合廃棄物類
本実施例において、改質処理素材に予め調製された参考例9に示した含水複合廃棄物類を選び、改質処理剤ならびに機能付加成分からなる複合改質処理剤を採択して一連の作業工程に付する改質方法により、含水複合廃棄物類に無害化処理ならびに形状化処理が施された構造体からなる接着形状体について説明する。
[Example 5] Water-containing composite wastes In this example, the water-containing composite wastes shown in Reference Example 9 prepared in advance as the reforming treatment material are selected, and a composite reforming agent composed of a reforming treatment agent and a function-added component is selected. A bonded shaped body composed of a structure obtained by detoxifying and shaping hydrous composite wastes by a modification method in which a quality treatment agent is adopted and subjected to a series of work steps will be described.

改質処理剤は参考例2に示した中から選び、機能付与剤は参考例5ないし8に示した中から選び、水系溶媒は水道水を選んだ。以上の種類と配合内容と活性化混和物のpH値を表24に併せ表示した。この時混和物は常温×10分間で調製し、養生条件は全て常温×28日で行い、試験用供試体は、実施例1に示した試験仕様に従って調製した。  The modifying agent was selected from those shown in Reference Example 2, the function-imparting agent was selected from those shown in Reference Examples 5 to 8, and tap water was selected as the aqueous solvent. The above types, blending contents, and pH value of the activated admixture are also shown in Table 24. At this time, the admixture was prepared at room temperature × 10 minutes, all curing conditions were performed at room temperature × 28 days, and the test specimens were prepared according to the test specifications shown in Example 1.

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調製した各円柱状の試験供試体における物性[水溶出pH、耐水性、耐熱性、一軸圧縮強度(q=KN/m)、クロムの中性域ならびに酸性域の溶出試験]を物性評価試験方法の項で示した試験方法に則りそれぞれ測定してそれぞれを評価した。
それらの結果を表25に併せ表示した。
Physical property evaluation test of physical properties [elution test of water elution pH, water resistance, heat resistance, uniaxial compressive strength (q = KN / m 2 ), neutral and acidic range of chromium] in each cylindrical test specimen prepared Each was measured according to the test method shown in the method section and evaluated.
The results are also shown in Table 25.

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以上の結果、含水汚泥類に対して、予め含水量の調整機能を兼ねて焼却灰を加え、次いで一連の作業工程により調製された構造体は、各処理対処素材に共存していたクロム等の有害金属が固定・不溶化され、所定の耐水性がある構造体に無害化処理ならびに形状化処理が施されており、有効に再資源化資材として提供できることが良く理解される。  As a result of the above, incinerated ash was added to water-containing sludges in advance to serve as a moisture content adjustment function, and then the structure prepared by a series of work steps was made of chromium, etc. It is well understood that harmful metals are fixed and insolubilized, and a structure having a predetermined water resistance is subjected to detoxification treatment and shaping treatment, and can be effectively provided as a recycling material.

[実施例6]S+骨材入り構造体
本実施例において、混合廃棄物類等を改質処理素材として改質処理剤と機能付与剤をワンパックした複合改質処理剤を採択して一連の作業工程に付する改質方法により、無害化処理と形状化処理が施された構造体からなる接着形状体について説明する。
[Example 6] S + Aggregate-containing structure In this example, a mixed reforming treatment agent in which one package of a reforming treatment agent and a function-imparting agent is adopted using mixed waste and the like as a reforming treatment material, and a series of A bonded shape body composed of a structure subjected to the detoxification process and the shaping process by the modification method applied to the work process will be described.

改質処理素材として混合廃棄物類を参考例1の中から選び、改質処理剤は参考例2に示した中から選び、機能付与剤は参考例5ないし8に示した中から選び、水系溶媒は水道水を選んだ。以上の種類と配合内容と活性化混和物のpH値を表26に併せ表示した。この時混和物は常温×10分間で調製し、養生条件は全て常温×28日で行い、試験用供試体は、実施例1に示した試験仕様に従って調製した。  The mixed waste is selected from the reference examples 1 as the reforming material, the reforming agent is selected from the examples shown in the reference example 2, the function-imparting agent is selected from the examples shown in the reference examples 5 to 8, and the aqueous system is selected. The solvent was tap water. The above types, blending contents, and pH values of the activated blends are shown together in Table 26. At this time, the admixture was prepared at room temperature × 10 minutes, all curing conditions were performed at room temperature × 28 days, and the test specimens were prepared according to the test specifications shown in Example 1.

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調製した各円柱状試験体をモールド型より脱型し、それぞれ円柱状試験供試体とした。各円柱状試験供試体の物性[水溶出pH、耐水性、耐熱性、一軸圧縮強度(q=KN/m)、セレンの中性域溶出試験]を物性評価試験方法の項で示した試験方法により測定してそれぞれ評価し、それらの結果を表26に併せ表示した。Each prepared cylindrical specimen was removed from the mold and used as a cylindrical specimen. Tests showing the physical properties of each cylindrical test specimen [water elution pH, water resistance, heat resistance, uniaxial compressive strength (q = KN / m 2 ), neutral area elution test of selenium] in the physical property evaluation test method section Each of the results was measured and evaluated, and the results are also shown in Table 26.

Figure 2006247645
Figure 2006247645

以上の結果、混合廃棄物類等を改質処理素材として、改質処理剤と機能付与剤で構成されてワンパック化された複合改質処理剤を採択して一連の作業工程に付する改質方法により、pH10未満で無害化処理が施され、6000KN/m以上の強度を確保しており、固化体強度発現が有効であることが良く理解される。As a result of the above, a modified reforming agent that is composed of a reforming treatment agent and a function-imparting agent and is made into a one-pack by using mixed wastes as a reforming treatment material is subjected to a series of work steps. It is well understood that the detoxification treatment is performed at a pH of less than 10 by the quality method, the strength of 6000 KN / m 2 or more is secured, and the solidified body strength expression is effective.

[実施例7]改質処理剤の配合量を変える
本実施例において、実施例4で採択した石炭灰(TSW02)と高炉スラグ(TSW07)の2者混合廃棄物(TSW14)を改質処理素材として、添加する改質処理剤の配合量を変化させ、さらに機能付与剤を加えて構成されてワンパック化された複合改質処理剤を採択して一連の作業工程に付する改質方法により、混合廃棄物に無害化処理ならびに形状化処理が施された構造体からなる接着形状体について説明する。
[Example 7] Changing the compounding amount of the reforming agent In this example, the two-component mixed waste (TSW14) of coal ash (TSW02) and blast furnace slag (TSW07) adopted in Example 4 is used as the reforming material. As a modification method, the compounding amount of the modifying treatment agent to be added is changed, and a composite modifying treatment agent that is configured by adding a function-imparting agent and formed into a one-pack is adopted and subjected to a series of work steps. The bonded shape body composed of a structure body obtained by detoxifying and shaping the mixed waste will be described.

改質処理剤は参考例2に示した中から選び、機能付与剤は参考例5ないし8に示した中から選び、水系溶媒は水道水を選んだ。以上の種類と配合内容と活性化混和物のpH値を表24に併せ表示した。この時混和物は常温×10分間で調製し、養生条件は全て常温×28日で行い、試験用供試体は、実施例1に示した試験仕様に従って調製した。  The modifying agent was selected from those shown in Reference Example 2, the function-imparting agent was selected from those shown in Reference Examples 5 to 8, and tap water was selected as the aqueous solvent. The above types, blending contents, and pH value of the activated admixture are also shown in Table 24. At this time, the admixture was prepared at room temperature × 10 minutes, all curing conditions were performed at room temperature × 28 days, and the test specimens were prepared according to the test specifications shown in Example 1.

Figure 2006247645
Figure 2006247645

調製した各円柱状の試験供試体における物性[水溶出pH、耐水性、耐熱性、一軸圧縮強度(q=KN/m)、クロムの中性域ならびに酸性域の溶出試験]を物性評価試験方法の項で示した試験方法に則りそれぞれ測定してそれぞれを評価した。
それらの結果を表25に併せ表示した。
Physical property evaluation test of physical properties [elution test of water elution pH, water resistance, heat resistance, uniaxial compressive strength (q = KN / m 2 ), neutral and acidic range of chromium] in each cylindrical test specimen prepared Each was measured according to the test method shown in the method section and evaluated.
The results are also shown in Table 25.

Figure 2006247645
Figure 2006247645

以上の結果、混合廃棄物類に対して、配合改質処理剤の配合量を本発明範囲内で変量した場合も、一連の作業工程により調製される構造体は、処理対処素材に共存していたクロム等の有害金属が固定・不溶化され、所定の耐水性がある構造体に無害化処理ならびに形状化処理が施されており、再資源化資材として提供できることが良く理解される。  As a result of the above, even when the blending amount of the blend-modifying treatment agent is varied within the scope of the present invention with respect to the mixed waste, the structure prepared by a series of work steps coexists in the treatment-measuring material. It is well understood that harmful metals such as chromium are fixed and insolubilized, and a structure having a predetermined water resistance is subjected to detoxification treatment and shaping treatment, and can be provided as a recycling material.

[実施例8]顆粒体で土木資材
本実施例において改質処理素材に各種の廃棄物類を選び、改質処理剤ならびに機能付加成分からなる複合改質処理剤を採択して一連の作業工程に付する改質方法により、廃棄物類に無害化処理ならびに形状化処理が施されて顆粒体に形状化された無公害型結着形状体について説明する。
[Embodiment 8] Civil engineering materials in granules In this embodiment, various wastes are selected as the reforming treatment material, and a composite reforming treatment agent composed of a reforming treatment agent and a function-added component is adopted. A non-polluting bound shaped body obtained by applying a detoxification process and a shaping process to wastes by a reforming method applied to the above to form a granule will be described.

改質処理素材として廃棄物類を参考例1に示した中から選び、改質処理剤を参考例2に示した中から選び、機能付与剤を参考例5ないし8に示した中から選び、水系溶媒は水道水を選んだ。以上の種類と配合内容と活性化混和物のpH値を表30に併せ表示した。この時混和物は常温×2時間で調製し、養生条件は全て常温×28日で行った。  Select the wastes as the modification treatment material from those shown in Reference Example 1, choose the modification treatment agent from among those shown in Reference Example 2, select the function-imparting agent from among those shown in Reference Examples 5 to 8, Tap water was selected as the aqueous solvent. The above types, blending contents, and pH value of the activated admixture are also shown in Table 30. At this time, the admixture was prepared at room temperature × 2 hours, and all curing conditions were performed at room temperature × 28 days.

本実施例における顆粒体からなる試験用供試体の調整は、選んだ材料1Kgをセメントモルタルの試験調製に使用されるセメントモルタル試験用ミキサーに採り、常温×約10分間撹拌混和・混練して可塑状ないしはモルタル状の活性化混和物に調製しつつ、さらに撹拌を続けて1ないしは7mmφの顆粒状に造粒し、常温×28日間の養生条件で養生した顆粒体をそれぞれの試験用供試体とした。  Preparation of the test specimen composed of granules in this example is carried out by taking 1 Kg of the selected material into a cement mortar test mixer used for cement mortar test preparation, stirring and mixing and kneading for about 10 minutes at room temperature and plasticizing. While stirring into a mortar-like activated admixture, stirring is continued and granulated into 1 to 7 mmφ granules, and the granules cured under normal temperature x 28-day curing conditions are used as test specimens. did.

Figure 2006247645
Figure 2006247645

調製した各試験用供試体の物性[水溶出pH、耐水性、耐熱性、顆粒体の強度試験(荷重重量)、鉛の中性域溶出試験]を物性評価試験方法の項で示した試験方法により測定し、それぞれ評価し、それらの結果を表31に併せ表示した。

Figure 2006247645
Test method showing physical properties [water elution pH, water resistance, heat resistance, granule strength test (load weight), neutral elution test of lead] in each physical property evaluation test method of each test specimen prepared Were measured and evaluated, and the results were also shown in Table 31.
Figure 2006247645

以上の結果、廃棄物類を改質処理素材として、本発明の改質処理剤ならびに機能付与剤を加えて調製した結着形状体は、耐水性で耐熱性があり、顆粒体の荷重強度が120Kg以上で形状化処理が施され、水溶出のpH値が10未満で鉛を固定・不溶化した無害化処理が施されている土木資材(盛土材、中込材、覆砂材、造成材、植栽用土材等)からなる再資源化資材として好適に提供されることが良く理解される。  As a result of the above, the binder-shaped body prepared by adding wastes as a modification treatment material and adding the modification treatment agent and the function-imparting agent of the present invention is water resistant and heat resistant, and the load strength of the granule is high. Civil engineering materials that are shaped at 120Kg or more and have a pH value of water elution of less than 10 and are treated with detoxification by fixing and insolubilizing lead (banking materials, intermediate materials, sand-capping materials, artificial materials, planting It is well understood that it is suitably provided as a resource recycling material consisting of soil materials for planting and the like.

[実施例9]不焼成の耐火材・耐熱材
本実施例において改質処理素材に廃棄物類を選び、改質処理剤および機能付与剤を採択して一連の作業工程に付する改質方法により、廃棄物類に無害化処理ならびに形状化処理が施されている耐火材・耐熱材に形状化されている結着形状体について説明する。
[Example 9] Non-fired refractory / heat-resistant material In this example, a reforming method in which wastes are selected as a reforming treatment material, a reforming treatment agent and a function-imparting agent are adopted, and a series of work steps are applied. Thus, a bonded shape body that is shaped into a refractory / heat-resistant material in which wastes are detoxified and shaped is described.

改質処理素材として高炉スラグとケイカル廃材を参考例1の中から選び、改質処理剤を参考例2に示した中から選び、機能付与剤は参考例5ないし8に示した中から耐熱火組成物等を選び、水系溶媒は水道水を選んだ。以上の種類と配合内容と活性化混和物のpH値を表32に併せ表示した。この時混和物は常温×10分間で調製し、養生条件は常温×28日で行い、試験用供試体は、実施例1に示した試験仕様に従って調製した。  Blast furnace slag and calcium waste are selected from the reference example 1 as the reforming material, the reforming agent is selected from those shown in the reference example 2, and the function-imparting agent is the heat resistant fire from among those shown in the reference examples 5 to 8. The composition and the like were selected, and tap water was selected as the aqueous solvent. The above types, blending contents, and pH value of the activated blend are also shown in Table 32. At this time, the admixture was prepared at room temperature x 10 minutes, the curing conditions were carried out at room temperature x 28 days, and the test specimen was prepared according to the test specifications shown in Example 1.

Figure 2006247645
Figure 2006247645

調製した各円柱状試験体をモールド型より脱型し、円柱状試験供試体とした。各円柱状試験供試体の物性[水溶出pH、耐水性、耐熱性の熱収縮減少率(%)、養生後の焼成前強度一軸圧縮強度(q=KN/m)、鉛の中性域溶出試験(mg/L)]を物性評価試験方法の項で示した試験方法により測定してそれぞれ評価し、それら結果を表33に併せ表示した。Each prepared cylindrical specimen was removed from the mold and used as a cylindrical specimen. Physical properties of each cylindrical test specimen [water elution pH, water resistance, heat-resistant heat shrinkage reduction rate (%), post-curing strength before firing uniaxial compressive strength (q = KN / m 2 ), neutral range of lead The dissolution test (mg / L)] was measured by the test methods shown in the physical property evaluation test method section and evaluated, and the results are also shown in Table 33.

Figure 2006247645
Figure 2006247645

以上の結果、本発明改質処理法により、廃棄物類に改質処理剤と機能付与剤である耐熱火組成物を付加し、水系溶媒を加えて調製した混和物を経由し、反応養生して調製した各接着形状体は、水溶出pH値が10未満を示して耐水性であり、焼成前の強度でも充分な強度を有し、熱収縮減少率も小さく、また焼成後の強度も充分にあり、耐火材・耐熱材・断熱材等として良好に供給されることが理解される。  As a result of the above, the modification treatment method of the present invention adds a modification treatment agent and a heat-resistant fire composition as a function-imparting agent to wastes, and a reaction curing process through an admixture prepared by adding an aqueous solvent. Each of the adhesive shaped bodies prepared in this manner is water resistant with a water elution pH value of less than 10, has sufficient strength even before firing, has a low rate of reduction in thermal shrinkage, and has sufficient strength after firing. Therefore, it is understood that it is satisfactorily supplied as a refractory material, a heat-resistant material, a heat insulating material or the like.

[実施例10]保温材・断熱材
本実施例において改質処理素材に廃棄物類を選び、改質処理剤および機能付与剤を採択して一連の作業工程に付する改質方法により、廃棄物類に無害化処理ならびに形状化処理が施されている保温材・断熱材に形状化されている結着形状体について説明する。
[Embodiment 10] Insulating material and heat insulating material In this embodiment, waste is selected as a reforming treatment material, and the disposal is performed by a reforming method in which a reforming treatment agent and a function-imparting agent are adopted and subjected to a series of work steps. The binding shape body shaped into the heat insulating material and heat insulating material in which the detoxification process and the shaping process are performed on the objects will be described.

改質処理素材としてケイカル廃材(トバモライト系ケイ酸カルシウム廃材)を参考例1の中から選び、改質処理剤を参考例2に示した中から選び、機能付与剤として断熱・保温組成物等を参考例5ないし8に示した中から選び、水系溶媒は水道水を選んだ。以上の種類と配合内容と活性化混和物のpH値を表34に併せ表示した。この時混和物は常温×10分間で調製し、養生条件は全て常温×28日で行い、試験用供試体は、実施例1に示した試験仕様に従って調製した。  Select the waste material for calcium treatment (tobermorite-based calcium silicate waste material) from Reference Example 1 as the modification treatment material, select the modification treatment agent from those shown in Reference Example 2, and select the heat insulation and heat insulation composition as the function-imparting agent. Selected from Reference Examples 5 to 8, tap water was selected as the aqueous solvent. The above types, blending contents, and pH value of the activated admixture are also shown in Table 34. At this time, the admixture was prepared at room temperature × 10 minutes, all curing conditions were performed at room temperature × 28 days, and the test specimens were prepared according to the test specifications shown in Example 1.

Figure 2006247645
Figure 2006247645

調製した各円柱状試験体をモールド型より脱型し、円柱状試験供試体とした。各円柱状試験供試体の物性[水溶出pH、耐水性、耐熱性の熱収縮減少率(%)、養生後の常態曲げ強度(q=N/mm)、かさ密度(g/cc)、鉛の中性域溶出試験(mg/L)]を物性評価試験方法の項で示した試験方法により測定してそれぞれ評価し、それらの結果を表35に併せ表示した。Each prepared cylindrical specimen was removed from the mold and used as a cylindrical specimen. Physical properties of each cylindrical test specimen [water elution pH, water resistance, heat-resistant heat shrinkage reduction rate (%), normal bending strength after curing (q = N / mm 2 ), bulk density (g / cc), The lead neutral zone dissolution test (mg / L)] was measured by the test method shown in the section of physical property evaluation test method and evaluated respectively. The results are also shown in Table 35.

Figure 2006247645
Figure 2006247645

以上の結果、本発明改質処理法により、廃棄物類に改質処理剤と機能付与剤である断熱・保温組成物を付加し、水系溶媒を加えて調製した混和物を経由し、反応養生して調製した各接着形状体は、水溶出pH値が10未満を示して耐水性であり、強度ならびにかさ密度が0.05ないしは1.2の範囲で650℃における熱収縮減少率が2.0%未満に確保されている保温材・断熱材等として良好に供給されることが理解される。  As a result of the above, according to the modification treatment method of the present invention, a heat treatment / heat insulation composition as a modification treatment agent and a function-imparting agent is added to wastes, and a reaction curing is performed via an admixture prepared by adding an aqueous solvent. Each of the adhesive shaped bodies prepared in this manner is water resistant with a water elution pH value of less than 10, and the thermal shrinkage reduction rate at 650 ° C. in the range of 0.05 to 1.2 in strength and bulk density is 2. It is understood that it is satisfactorily supplied as a heat insulating material, a heat insulating material, etc. secured to less than 0%.

[実施例11]養生温度変化
本実施例において改質処理素材に廃棄物類を選び、改質処理剤および機能付与剤を採択して所定条件下で調製した混和物を付する養生工程において、養生条件を変化させて廃棄物類に無害化処理ならびに形状化処理が施されている再資源化資材からなる結着形状体について説明する。
[Example 11] Curing temperature change In the curing process of selecting wastes as the reforming treatment material in this example, applying the reforming treatment agent and the function-imparting agent, and attaching the mixture prepared under predetermined conditions, A binding shape body made of a recycled material in which the curing conditions are changed and the wastes are detoxified and shaped is described.

改質処理素材として混合廃棄物である石炭灰(TSW02)100質量部と高炉スラグ(TSW07)100質量部の等量混合廃棄物(TSW14)を選んだ。改質処理剤は参考例2に示したA−01を選び、機能付与剤は参考例5ないし8に示した中から選び、水系溶媒は水道水を選んだ。以上の種類と配合内容と活性化混和物のpH値を表36に併せ表示した。この時混和物は常温×24時間で調製した。ついで実施例1に示した試験仕様に従って調製したプラスチック製モールド型(φ50×100mmの円柱状)に充填した円柱状試験体を表36に示す養生条件により試験用供試体を調製した。  As a reforming treatment material, an equivalent mixed waste (TSW14) of 100 parts by mass of coal ash (TSW02) and 100 parts by mass of blast furnace slag (TSW07), which is a mixed waste, was selected. A-01 was selected as the modifying agent, as shown in Reference Example 2, the function-imparting agent was selected from those shown in Reference Examples 5 to 8, and tap water was selected as the aqueous solvent. The above types, blending contents, and pH values of the activated blends are also shown in Table 36. At this time, the mixture was prepared at room temperature × 24 hours. Next, test specimens for testing were prepared under the curing conditions shown in Table 36 for cylindrical specimens filled in plastic molds (φ50 × 100 mm cylinders) prepared according to the test specifications shown in Example 1.

Figure 2006247645
Figure 2006247645

実施例1に示した試験仕様に従って調製した各円柱状試験体をモールド型より脱型し、円柱状試験供試体とした。各円柱状試験供試体の物性「水溶出pH、耐水性、耐熱性、一軸圧縮強度(q=KN/m)、鉛の中性域溶出試験(mg/L)]を物性評価試験方法の項で示した試験方法により測定してそれぞれ評価し、それらの結果を表37に併せ表示した。Each cylindrical test specimen prepared according to the test specifications shown in Example 1 was removed from the mold and used as a cylindrical test specimen. Properties of each cylindrical test specimen “water elution pH, water resistance, heat resistance, uniaxial compressive strength (q = KN / m 2 ), lead neutral zone elution test (mg / L)” Each measurement was performed by the test method shown in the section and evaluated, and the results are also shown in Table 37.

Figure 2006247645
Figure 2006247645

以上の結果、本発明改質処理法により、混合廃棄物類に改質処理剤と機能付与剤を付加して水系溶媒を介して調製した混和物を大気、蒸気、水中の各温度条件下で養生して調製した各接着形状体は、水溶出pH値が10未満を示して耐水性で耐熱性の決着形状化対として良好に供給されることが理解される。  As a result of the above, the modified treatment method of the present invention adds the modifying treatment agent and the function-imparting agent to the mixed wastes and the mixture prepared through the aqueous solvent under the temperature conditions of air, steam, and water. It is understood that each bonded shape body prepared by curing exhibits a water elution pH value of less than 10 and is well supplied as a water-resistant and heat-resistant fixed shape pair.

[実施例12]膜状・フイルム
本実施例において改質処理素材に廃棄物類を選び、改質処理剤および機能付与剤を採択して調製される可塑性ないしは流動性の糊状混和物を活用して、無害処理が施されているフイルム状に形状化処理されている無公害型接着形状体の調製について説明する。
[Example 12] Film / film In this example, a plastic or fluid paste mixture prepared by selecting wastes as the reforming material and adopting the reforming agent and the function-imparting agent is used. Then, the preparation of a pollution-free adhesive shaped body that has been shaped into a film that has been subjected to a harmless treatment will be described.

改質処理素材として人工合成品であるTSM03ならびにケイカル廃材(トバモライト系ケイ酸カルシウム廃材)を参考例1の中から選び、改質処理剤を参考例2に示した中から選び、機能付与剤としては充填材を参考例7の中から選び、水系溶媒は水道水を選び、以上の種類と配合内容、活性化混和物のpH値を表38に併せ表示した。以上の材料を10分間混和して、可塑性ないしは流動性の糊状混和物を調製した。  Artificial synthetic products TSM03 and calcium waste (tobermorite calcium silicate waste) are selected from Reference Example 1 as the modification treatment material, and the modification treatment agent is selected from those shown in Reference Example 2 as a function-imparting agent. Selected a filler from Reference Example 7, tap water was selected as the aqueous solvent, and the above types, blending contents, and pH value of the activated admixture were also shown in Table 38. The above materials were mixed for 10 minutes to prepare a plastic or fluid paste mixture.

調製した糊状混和物によるフイルム状の膜状品は,ガラス繊維により製造された織布(重量:149g/m、厚さ:0.2mm、幅:92cm)を基材に選び、この基材のガラス繊維織布の両面に調製した糊状混和物を含浸させながらプラスチックス製フイルムの上で全体約4mm厚さに塗布し、約常温×28日間放置して水硬性反応を完結せしめる養生工程にてガラス繊維織布を基材とする無機質フイルムを加工調製した。The film-like film-like product prepared from the paste-like admixture was selected from a woven fabric (weight: 149 g / m 2 , thickness: 0.2 mm, width: 92 cm) made of glass fiber. Applying a total thickness of about 4 mm on a plastic film while impregnating the paste-like mixture prepared on both sides of the glass fiber woven fabric, leaving it at room temperature for 28 days to complete the hydraulic reaction In the process, an inorganic film based on a glass fiber woven fabric was processed and prepared.

Figure 2006247645
Figure 2006247645

ここに調製した無機質フイルムにおける物性評価を物性試験方法に則り、耐水性ならびに水溶出pHを測定しまた、耐熱性の確認試験は、ガラス繊維織布を基材とする無機質フイルムの試験片(タテ50mm×ヨコ100mm)を400℃の電気加熱オーブン中に2時間放置暴露し、暴露後の試験体状態を観察し、引張加重試験における初期最大荷重と加熱曝露後の最大荷重(Kg)を測定し、そのときの引張時の荷重減少率を求めて評価した。その結果を表39に併せ表示した。  The physical properties of the inorganic film prepared here were evaluated according to the physical property test method, and the water resistance and water elution pH were measured. The heat resistance confirmation test was conducted using a test piece (vertical length) of a glass fiber woven fabric as a base material. 50mm x 100mm) is left exposed in an electric heating oven at 400 ° C for 2 hours, the state of the specimen after exposure is observed, and the initial maximum load in the tensile load test and the maximum load (Kg) after heat exposure are measured. Then, the load reduction rate at the time of tension was obtained and evaluated. The results are also shown in Table 39.

Figure 2006247645
Figure 2006247645

以上の結果、調整した無機質フイルムは耐水性で水溶出pHが9.0であり、有害物質の鉛溶出が固定化されており、フイルムの引っ張り加重は、98Kg(タテ50×ヨコ100mm)であり、耐熱性の確認試験では、異常なく荷重減少率が30%の範囲であり、耐熱・断熱性のフイルム素材等として良好に供給されることが理解される。  As a result of the above, the prepared inorganic film is water resistant and has a water elution pH of 9.0, the lead elution of harmful substances is fixed, and the tensile load of the film is 98 Kg (vertical 50 × width 100 mm). In the heat resistance confirmation test, it is understood that the load reduction rate is in the range of 30% without any abnormality, and that the film can be satisfactorily supplied as a heat-resistant and heat-insulating film material.

[実施例13]基材積層複合品
本実施例において、予め調製した可塑性ないしは流動性の糊状混和物を予め用意したセメントからなる応用対象基材に塗布・被覆・結着せしめて調製した基材積層複合品からなる耐水性の結着形状体について説明する。
[Example 13] Substrate-laminated composite product In this example, a base prepared by applying, coating, and binding a previously prepared plastic or flowable paste-like admixture to an application target substrate made of cement prepared in advance. A water-resistant binding shape body made of a laminated material composite material will be described.

改質処理素材として混合廃棄物(TSW14)を選び、改質処理剤を参考例2に示した中から選び、機能付与剤としては充填材を中心参考例7の中から選び、水系溶媒として水道水を選び、以上の種類と配合内容、調製混和物のpH値を表40に併せ表示した。以上の材料を10分間混和して、可塑性ないし流動性の活性化混和物を調製した。  Mixed waste (TSW14) is selected as the reforming material, the modifying agent is selected from those shown in Reference Example 2, the filler is selected from the central reference example 7 as the function-imparting agent, and tap water is used as the aqueous solvent. Water was selected, and the above types, blending contents, and pH values of the prepared blends were shown together in Table 40. The above materials were mixed for 10 minutes to prepare a plastic or flowable activated mixture.

Figure 2006247645
Figure 2006247645

本実施例における応用対象基材としては、ケイカル製スレート板により調製された長方形状(210×100×6cm)厚板状片を選んだ。この厚板状片の表面に糊状混和物を約5mm厚に塗布し、それぞれ基材積層複合物とした。これらの基材積層複合物を常温×28日の養生工程を経て基材積層複合品とし、各基材積層複合品を物性評価試験方法に準拠して付着試験体として評価した。  As an application target base material in this example, a rectangular (210 × 100 × 6 cm) thick plate-shaped piece prepared by a slate plate made of calcium was selected. A paste-like admixture was applied to the surface of this thick plate-like piece to a thickness of about 5 mm to obtain a base laminate composite. These base material laminate composites were subjected to a curing process at room temperature × 28 days to obtain base material laminate composite products, and each base material laminate composite product was evaluated as an adhesion test specimen in accordance with a physical property evaluation test method.

付着試験体の物性試験は、耐水性および耐熱性を確認し、さらに水溶出pH値を測定した。また、物性評価試験方法の項に示した付着力試験に準拠して、鋼板とケイカル製スレート板を基材として、鋼板とケイカル製スレート板の所定面積に所定量の糊状混和物からなる接着剤を塗って付着力試験用の付着試験体を調製した試験体を養生工程[約20℃の常温に28日間放置]に付して付着力測定用付着試験体し、試験体の剪断破壊強度[KN/m]、さらに鉛溶出試験をそれぞれ測定した。
それらの結果を表41併せ表示した。
In the physical property test of the adhesion test body, water resistance and heat resistance were confirmed, and the water elution pH value was further measured. In addition, in accordance with the adhesion test shown in the section of physical property evaluation test method, using a steel plate and a calcium slate plate as a base material, an adhesive comprising a predetermined amount of paste-like admixture on a predetermined area of the steel plate and the calcium slate plate The test specimen prepared by applying a coating agent for the adhesion test was subjected to a curing process [left at room temperature of about 20 ° C. for 28 days] to form an adhesion test specimen for measuring the adhesive strength, and the shear fracture strength of the test specimen [KN / m 2 ] and a lead elution test were measured respectively.
The results are also shown in Table 41.

Figure 2006247645
Figure 2006247645

以上の結果、混合廃棄物に改質処理剤と粒径100μ以下の粉末充填材と水道水とで均質混和した糊状混和物による接着剤により調製した付着試験体は、耐水性および耐熱性を有しおり、水溶出pH値が10未満に鉛が不溶化されて無害化されており、付着力(剪断破壊強度)が2,500KN/m以上であり、被覆・付着体として有効に供給されることが理解される。As a result of the above, the adhesion test specimen prepared by the adhesive with the paste-like admixture that was homogeneously mixed with the modified treatment agent, the powder filler having a particle size of 100 μm or less and tap water to the mixed waste has water resistance and heat resistance. It has a water elution pH value of less than 10 and is insolubilized by insolubilization. Adhesive strength (shear fracture strength) is 2,500 KN / m 2 or more, and it is effectively supplied as a coating / adhesive. It is understood.

[実施例14]耐酸性基材積層複合品
本実施例において、予め調製した可塑性ないしは流動性の糊状混和物を予め用意したケイカル製スレート板を基材として塗布・被覆・結着せしめて調製した基材積層複合品からなる耐酸性の結着形状体について説明する。
[Example 14] Laminated composite product with acid-resistant base material In this example, prepared by coating, coating and binding a pre-prepared plastic or flowable paste-like admixture with a calcium slate plate prepared in advance. The acid-resistant binding shape body which consists of the base-material laminated composite goods which were made is demonstrated.

改質処理素材としては参考例1からフライアッシュを選び、改質処理剤に塩基性ケイ酸ソーダを中心とする改質処理剤を選び、機能付与剤としてレインホースメントの川砂(φ0.5〜4mm)またはサプリメントの粉末ケイ酸ソーダ、インプルーブメントのカオリン等を選び、水系溶媒に水道水を選び、以上の種類と配合内容、調製した混和物pH値を表42に併せ表示した。以上の材料を10分間混和して、予め可塑性ないしは流動性の糊状混和物を調製した。  The fly ash is selected from Reference Example 1 as the modification treatment material, the modification treatment agent mainly composed of basic sodium silicate is selected as the modification treatment agent, and the river sand of rain reinforcement (φ0.5 ~ 4 mm) or supplemented powdered sodium silicate, improvement kaolin, etc., tap water was selected as the aqueous solvent, and the above types, blended contents, and prepared blend pH values were also shown in Table 42. The above materials were mixed for 10 minutes to prepare a plastic or fluid paste mixture in advance.

Figure 2006247645
Figure 2006247645

円柱状試験体に成型し、室温に7日間放置して耐酸材料としての円形状処理試験体を作成した。調製した各円柱状処理試験体における物性評価を耐水性、水溶出pHならびにpH3の酸性溶液に浸漬したときの耐酸材料強度保持率を測定し、さらに複合型ではアスベスト板と鉄鋼板とを基材としてモルタル状混和物を被覆材として付着力試験の項記載の方法で付着試験体を調整して剪断破壊強度(KN/m)で測定して評価した。
その結果を表43に併せ表示した。
Molded into a cylindrical test specimen and allowed to stand at room temperature for 7 days to prepare a circular processed specimen as an acid resistant material. The physical properties of each prepared cylindrical specimen were measured for water resistance, water elution pH, and acid-resistant material strength retention when immersed in an acidic solution of pH 3, and in the composite type, asbestos plate and steel plate were used as base materials. As a coating material, mortar-like admixture was used as a coating material, and the adhesion test specimen was prepared by the method described in the section of the adhesion test, and the shear fracture strength (KN / m 2 ) was measured and evaluated.
The results are also shown in Table 43.

Figure 2006247645
Figure 2006247645

以上の結果、本発明改質処理剤を活用し、必要に応じてケイ酸アルカリを処理対象物として処理調製された活用品は、pH3酸性溶液に浸漬した耐酸性の基材積層複合品に変化がなく、耐水性で耐熱性であり、しかも耐酸性であることから化学工場、食品工場、厨房、温泉場等の耐酸性が求められる場所に有効に供給できることが理解される。  As a result of the above, the utilization product prepared by using the modified treatment agent of the present invention and treating with alkali silicate as a treatment target as required is changed to an acid-resistant base laminate composite product immersed in an acidic solution of pH 3 It is understood that it can be effectively supplied to places where acid resistance is required, such as chemical factories, food factories, kitchens, and hot springs.

[実施例15]活性粉体結着品
本実施例において、比表面積100m/g以上を有する吸着性粉粒体からなる応用対象基材表面に予め用意した流動性活性化混和物で濡らしつつ付着化処理物を経由する一連の作業工程により、予め調製されている流動性の活性化混和物が応用対象基材と固結一体化されて吸着性が確保されている付着型の結着形状体について説明する。
[Example 15] Active powder-bound product In this example, while wetted with a fluidized activated admixture prepared in advance on the surface of an application target substrate composed of an adsorbent granular material having a specific surface area of 100 m 2 / g or more. Adhesion-type binding shape in which a fluidized activated admixture prepared in advance is consolidated and integrated with the target substrate through a series of work steps that pass through the processed adhesive. Explain the body.

予め調製される流動性の活性化混和物は、混合廃棄物(TSW14)を処理対象素材に選び、改質処理剤に参考例2に示した中から選び、機能付与剤としては充填材を中心に参考例7の中から選び、水系溶媒として水道水を選び10分間混和して可塑性ないし流動性の活性化混和物を調製した。以上の種類と配合内容、調製混和物のpH値を表44に併せ表示する。  For the fluidized activated admixture prepared in advance, the mixed waste (TSW14) is selected as the material to be treated, the modification treatment agent is selected from those shown in Reference Example 2, and the function-imparting agent is mainly a filler. And selected from Reference Example 7, tap water was selected as an aqueous solvent and mixed for 10 minutes to prepare a plastic or fluid activated mixture. The above types, blending contents, and pH value of the prepared blend are also displayed in Table 44.

応用対象基材となる吸着性粉粒体としては、参考例7に示したファンクションメントの担持吸着組成物より選び、比表面積(m/g)と共に表44に示した。本実施例の活性粉体結着品として顆粒体に造粒には、中央に回転攪拌軸羽を有するタタライ型セメントモルタル混合機[φ100×0.5cmのタライ型]に表44に示した量割合で予め調製した混和物を吸着性粉粒体に加えて約10分間混合攪拌して全体を混和物としながら2ないし10mmφの粒径に混和・造粒された顆粒体を調製し、次いで常温かける28日間大気中に放置する養生工程に付する方法により改質処理した。The adsorptive powder particles used as the application target substrate were selected from the supported adsorption composition of the functionment shown in Reference Example 7 and shown in Table 44 together with the specific surface area (m 2 / g). The amount shown in Table 44 in a Tatarai type cement mortar mixer [φ100 × 0.5 cm Tarai type] having a rotary stirring shaft blade in the center for granulation into granules as the active powder binder of this example. Add the admixture prepared in advance to the adsorbent granules and mix and agitate for about 10 minutes to prepare the granule mixed and granulated to a particle size of 2 to 10 mmφ while making the whole admixture. The reforming process was carried out by a method that was subjected to a curing process that was allowed to stand in the atmosphere for 28 days.

Figure 2006247645
Figure 2006247645

ここに改質処理した顆粒体からなる活性粉体結着品について、物性評価試験方法にしたがい水溶出pH,耐水性、耐熱性、顆粒体荷重強度(kg)ならびに比表面積減少率(%)をそれぞれ測定して評価した。その結果を表45に併せ表示した。  For the active powder binders composed of the modified granules, water elution pH, water resistance, heat resistance, granule load strength (kg) and specific surface area reduction rate (%) according to the physical property evaluation test method Each was measured and evaluated. The results are also shown in Table 45.

Figure 2006247645
Figure 2006247645

以上の結果、予め調製した活性化混和物により比表面積が100m/g以上の吸着性を有する吸着性粉体と水とで固結一体化された顆粒体とするとき、吸着性粉体が有する比表面積が活性化混和物からなるバインダーで潰されることなく取り扱いやすい顆粒体は、比表面積減少率が20%以下に確保され、水溶出pH値が10未満であり、耐水・耐熱性を有している活性粉体結着品からなる結着形状体に改質処理されることが良く理解される。As a result of the above, when the adsorbent powder consolidated into the adsorbent powder having a specific surface area of 100 m 2 / g or more and water with the activated admixture prepared in advance is obtained, Granules that have a specific surface area that is easy to handle without being crushed by a binder made of an activated admixture has a specific surface area reduction rate of 20% or less, a water elution pH value of less than 10, and water and heat resistance. It is well understood that the modified shape is formed into a binding shape body made of the active powder binding product.

[実施例16]汚染土壌
本実施例において、改質処理素材として複数重金属類で汚染されている土壌地盤の汚染土壌を選び、該汚染土壌に対して水を介して改質処理剤を混和する一連の作業工程からなる改質処理方法により重金属類が固定・不溶化されて無害化処理されている原位置非成型品である耐水性の結着形状体について説明する。
[Example 16] Contaminated soil In this example, contaminated soil of soil ground contaminated with multiple heavy metals is selected as a reforming treatment material, and a modifying treatment agent is mixed with the contaminated soil through water. A water-resistant bonded shaped body, which is an in-situ non-molded product in which heavy metals are fixed and insolubilized by a reforming method consisting of a series of work steps and detoxified, will be described.

本実施例における改質処理剤としては、参考例2に示した改質処理剤(試料番号A−05)を選んだ。本実施例において採択した水系溶媒は、井戸水を選んだ。
また、本発明を従来技術と比較するための比較例として、市販ポルトランドセメントを比較改質処理剤として選んだ。
As the modification treatment agent in this example, the modification treatment agent (sample number A-05) shown in Reference Example 2 was selected. Well water was selected as the aqueous solvent adopted in this example.
Moreover, as a comparative example for comparing the present invention with the prior art, commercially available Portland cement was selected as a comparative modification treatment agent.

本実施例において改質処理素材とした汚染土壌は、化学工場跡地2カ所より採取した複数の重金属類[カドミ、鉛、ヒ素クロム、水銀]で汚染されている汚染土壌[土壌Aならびに土壌B]を選んだ。土壌Aならびに土壌Bの主成分[乾燥物基準で質量%]ならびに共存している重金属類(mg/kg)濃度を表44に併せ表示した。また、未処理状態にある土壌Aならびに土壌BにおけるpH7溶出試験ならびにpH4溶出試験による結果を表46に併せ表示した。  In this example, the contaminated soil used as the reforming material is contaminated soil [soil A and soil B] contaminated with a plurality of heavy metals [cadmium, lead, arsenic chromium, mercury] collected from two sites of the chemical factory. I chose. The main components of soil A and soil B [mass% based on dry matter] and the concentrations of coexisting heavy metals (mg / kg) are also shown in Table 44. Table 46 also shows the results of the pH 7 dissolution test and the pH 4 dissolution test on soil A and soil B in an untreated state.

Figure 2006247645
Figure 2006247645

汚染土壌に共存する重金属類が固定・不溶化されて無害化処理される原位置非成型品とする作業工程における混和工程において、改質処理素材の汚染土壌に対して、表47に示す配合割合で、改質処理剤(A−05)と水系溶媒(井戸水)を加え、かき混ぜ混和装置の試験用モルタルミキサー[マイティ30(容量20リッター:攪拌60rpm):(株)愛工舎製作所]を用いて攪拌混合してバサバサで可塑性の混和物とした。次いで混和物を原位置の大気中に放置する養生工程に付し、混和物を密封容器に採り室温(約25℃)で3日間放置後ならびに2ヶ月間放置養生後にそれぞれサンプリングして原位置非成型品である重金属類溶出試験等用の分析供試料とした。  In the mixing process in the in-situ non-molded product in which heavy metals coexisting in the contaminated soil are fixed, insolubilized and rendered innocuous, the blending ratio shown in Table 47 with respect to the contaminated soil of the modified material Then, the modification treatment agent (A-05) and an aqueous solvent (well water) are added, and the mixture is stirred using a mortar mixer for testing the mixing and mixing apparatus [Mighty 30 (capacity 20 liters: stirring 60 rpm): Aikosha Seisakusho Co., Ltd.]. The mixture was mixed into a plastic mixture. The mixture is then subjected to a curing process in which it is left in the original atmosphere, the mixture is placed in a sealed container, left at room temperature (about 25 ° C.) for 3 days, and then left for 2 months. It was used as an analytical sample for elution testing of heavy metals as molded products.

また、比較改質処理剤であるポルトランドセメントを本実施例の無害化処理と同様の改質方法により、汚染土壌Aならびに汚染土壌Bを対象にして表47に示す配合割合でセメントを混和して混和物とし、密封容器に取り室温で3日間放置および2ヶ月間放置養生後にサンプリングして重金属類溶出試験分析等用の供試料とした。  Further, Portland cement, which is a comparative modification treatment agent, was mixed in the blending ratio shown in Table 47 for the contaminated soil A and the contaminated soil B by the same modification method as the detoxification treatment of this example. The mixture was placed in a sealed container, left at room temperature for 3 days, and left for 2 months. After sampling, it was sampled as a sample for heavy metal dissolution test analysis.

Figure 2006247645
Figure 2006247645

Figure 2006247645
Figure 2006247645

Figure 2006247645
Figure 2006247645

本実施例で無害化処理された供試料における物性評価を確認するために、重金属類のpH7ならびにpH4における溶出試験(mg/L)を行い、その結果を表48および49に示した。また簡易型変形性測定試験[q=KN/m]による簡易型変形性ならびに水溶出pHについて試験を行い、その結果を表50にそれぞれ併せ表示した。In order to confirm the evaluation of physical properties of the samples subjected to the detoxification treatment in this example, dissolution tests (mg / L) of heavy metals at pH 7 and pH 4 were performed, and the results are shown in Tables 48 and 49. Further, tests were conducted on simple deformability and water elution pH by a simple deformability measurement test [q = KN / m 2 ], and the results are also shown in Table 50.

Figure 2006247645
Figure 2006247645

以上の結果、有害な重金属類が環境基準を超えて溶出している汚染土壌に対して、本発明改質処理剤を活用して原位置で改質処理して汚染土壌を常温で無害化処理するとき、共存する複数重金属類が本発明改質処理方法により同時に環境基準の範囲内で無害化処理され、しかも酸性雨を想定するpH4の溶液にも固定化された重金属類は溶出せず、水溶出pHが10未満で耐水性の原位置非成型品とした処理土壌とし、しかもコンクリート化されていない処理土壌地盤で即再利用が可能であることが良く理解される。  As a result of the above, contaminated soil from which harmful heavy metals are eluted exceeding the environmental standards is modified in situ using the modified treatment agent of the present invention, and the contaminated soil is detoxified at room temperature. In this case, the coexisting multiple heavy metals are simultaneously detoxified within the range of the environmental standard by the reforming treatment method of the present invention, and the heavy metals immobilized in the pH 4 solution assuming acid rain do not elute, It is well understood that the treated soil is an in-situ water-resistant unmolded product with a water elution pH of less than 10, and can be immediately reused on treated soil ground that is not concreted.

しかし、従来技術におけるセメントにより汚染土壌を処理する時は、共存する重金属類を一時的に被覆することは可能であっても、汚染土壌のpH値はアルカリ性であり重金属類を特に酸性域において固定・不溶化することはできず、長期(2ヶ月間)に放置されていると重金属類は環境に水溶出して環境基準を超える値となり、本発明技術と異なり、セメントでは汚染土壌共存の重金属類を安全に不溶化することはできていない。  However, when treating contaminated soil with cement in the prior art, the pH value of the contaminated soil is alkaline, even if it is possible to temporarily cover the coexisting heavy metals, and the heavy metals are fixed particularly in the acidic range. -If it cannot be insolubilized and left for a long period (two months), heavy metals will elute into the environment and will exceed the environmental standards. Unlike the technology of the present invention, heavy metals coexisting with contaminated soil will be used in cement. It cannot be insolubilized safely.

[実施例17]汚染土壌の現場
本実施例において、改質処理素材として複数重金属類が共存している原位置の汚染土壌地盤を対象として、本発明の一連の作業工程により原位置で共存重金属類を不溶化して無害化処理されている耐水性の結着形状体について説明する。
[Example 17] On-site of contaminated soil In this example, the heavy metal coexisting in-situ by the series of work steps of the present invention for the contaminated soil ground in which a plurality of heavy metals coexist as reforming treatment materials. A water-resistant binder-shaped body that has been insolubilized by detoxification is described.

本実施例における改質処理剤としては、参考例2に示した改質処理剤(試料番号A−05)を選んだ。本実施例において採択した水系溶媒は、近くの河川の水を利用した。本実施例にいて改質処理素材とした汚染土壌は、化学工場跡地より採取した複数重金属類[カドミ、鉛、ヒ素クロム、水銀]で汚染されている汚染土壌[土壌C地盤:10m×30m×深さ2m]を選んだ。土壌C地盤地区より採取したサンプリング土壌の分析結果の平均値による主成分[乾燥物基準で質量%]ならびに含有重金属類[mg/kg]濃度を表51に併せ表示した。また、未処理土壌Cにおける重金属類のpH7およびpH4の溶出試験を行い、結果を表52に併せ表示した。  As the modification treatment agent in this example, the modification treatment agent (sample number A-05) shown in Reference Example 2 was selected. The water-based solvent adopted in this example used water from a nearby river. In this example, the contaminated soil used as the modified material is contaminated soil contaminated with multiple heavy metals [cadmium, lead, arsenic chromium, mercury] collected from the site of the chemical factory [soil C ground: 10 m × 30 m × Depth 2m] was selected. Table 51 shows the main component [mass% based on dry matter] and the concentration of heavy metals [mg / kg] contained in the average value of the analysis results of the sampling soil collected from the soil C ground area. Moreover, the elution test of pH7 and pH4 of heavy metals in the untreated soil C was conducted, and the results are shown together in Table 52.

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本発明改質処理剤を活用した原位置汚染土壌地盤における共存重金属類を固定・不溶化する作業工程の混和工程には、土木業界における地盤改良等で汎用されている混和装置である「自走式土質改良方式」ならびに「バックホウ攪拌方式」の2方式を採択した。  In the mixing process of the work process of fixing and insolubilizing the coexisting heavy metals in the in situ contaminated soil ground using the modified treatment agent of the present invention, the “self-propelled type” is a mixing apparatus widely used for ground improvement in the civil engineering industry. Two methods were adopted: “Soil Improvement Method” and “Backhoe Stirring Method”.

混和工程の「自走式土質改良方式」での汚染土壌の改質は、RETERRA装置[コマツ社製:定格出力107KW/195rpm、混合方式:ソイルカッター+3軸大型ロータリーハンマー+アフターカッター]を原位置地盤に設置し、設置したRETERRA装置に原位置で採掘した汚染土壌を投入し、投入した汚染土壌1mに対して、改質処理剤(A−09)100kgの配合割合で改質処理剤を加え、さらに河川水を汚染土壌1mに対して、約80ないしは100kgを加えて連続的に混和し、混和物を採掘原位置に戻し、採掘原位置に戻した状態の常温で3日間放置する養生工程に付し、共存重金属類の固定・不溶化せしめて無害化処理を行った。For the improvement of contaminated soil using the “Self-propelled soil improvement method” in the mixing process, the RETERRA equipment [manufactured by Komatsu: rated output 107 KW / 195 rpm, mixing method: soil cutter + 3-axis large rotary hammer + aftercutter] Installed on the ground, put the contaminated soil mined in-situ into the installed RETERRA equipment, and apply the modified treatment agent at a mixing ratio of 100 kg of the modified treatment agent (A-09) to 1 m 3 of the introduced contaminated soil. In addition, about 80 to 100 kg of river water is added to 1 m 3 of contaminated soil and mixed continuously. The mixture is returned to the mining site and left at room temperature for 3 days. In the curing process, the coexisting heavy metals were fixed and insolubilized and detoxified.

混和工程の「バックホウ攪拌方式」での汚染土壌の改質は、バックホウ装置[コマツ製作所製、キャタビラ移動可能で平積:0.6mで山積:0.8m容量のバケットに攪拌機を付属させている]を現地に持ち込み、予め汚染土壌地盤に深さ1mを想定した深さ容量の土壌1mに対して、改質処理剤100kgの配合割合で改質処理剤を加えて、さらに河川水を汚染土壌1mに対して、約80ないしは100kgを加えてバックホウで均質混和し、混和された原位置に3日間放置する養生工程に付し、共存重金属類の固定・不溶化せしめて無害化処理を行った。Modification of contaminated soil in the "backhoe stirring method" mixing step, backhoe implement [Komatsu Seisakusho, Kyatabira movable flat product: piling at 0.6 m 3: it is supplied with a stirrer 0.8 m 3 volume of the bucket bringing it has] a local, previously contaminated with respect to soil 1m 3 depth capacity assuming the depth 1m soil ground, in addition to modifying agent in a proportion of the modifying treatment agent 100 kg, further river water against the contaminated soil 1 m 3, uniformly and intimately with backhoe added about 80 or 100 kg, subjected to curing step of standing 3 days admixed an original position, detoxification and allowed fixing and insolubilizing the coexistence heavy metals Went.

本実施例において、汚染土壌地盤原位置常温における「自走式土質改良方式」ならびに「バックホウ攪拌方式」により無害化処理された非成型処理物の物性評価を確認するために、物性評価試験方法の項記載の重金属類のpH7ならびにpH4における溶出試験により、重金属類の溶出量(mg/L)を測定し、その結果を表53に併せ示した。  In this example, in order to confirm the physical property evaluation of the non-molded processed material detoxified by the “self-propelled soil improvement method” and the “backhoe stirring method” at the normal temperature of the contaminated soil ground, The elution amount (mg / L) of heavy metals was measured by the dissolution test of heavy metals described in the section at pH 7 and pH 4, and the results are also shown in Table 53.

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以上の結果、複数の重金属類で汚染されている土壌地盤の原位置において、本発明改質処理剤により、「自走式土質改良方式」ならびに「バックホウ攪拌方式」による常温における一連の作業工程からなる改質方法により、共存する複数の重金属類が同時に無害化処理され、汚染土壌地盤が再利用可能な地盤状態に原位置において低コストで修復されていることが良く理解される  As a result of the above, in the original position of the soil ground contaminated with a plurality of heavy metals, the modified treatment agent of the present invention enables a series of work processes at room temperature by the “self-propelled soil improvement method” and the “backhoe stirring method”. It is well understood that the coexisting heavy metals are detoxified at the same time, and the contaminated soil ground is restored to a reusable ground condition at low cost in situ

[実施例18]ダイオキシン類含有の汚染土壌
本実施例において、ダイオキシン類含有の汚染土壌を改質処理素材として、改質処理剤を均質に混和して、汚染土壌含有の水を介する常温における一連の作業工程により含有ダイオキシン類を捕捉・分解せしめて無公害化処理して処理調製した耐水性の結着形状体について説明する。
[Example 18] Dioxin-Containing Contaminated Soil In this example, a dioxin-containing contaminated soil was used as a reforming treatment material, and a reforming treatment agent was homogeneously mixed, and a series at normal temperature via contaminated soil-containing water. The water-resistant binding shape body prepared by capturing and decomposing the contained dioxins by the above-mentioned work process and making it non-polluting treatment and treating it will be described.

本実施例における改質処理素材の汚染土壌としては、ごみ焼却場跡地より採取したダイオキシン類で汚染されている汚染土壌[土壌D]を選んだ。土壌Dにおけるダイオキシン類による汚染状況は、含有ダイオキシン類の濃度を物性評価試験方法の項に記載の簡易分析測定法に従い測定し、その結果を表54にpg−TEQ/g濃度で表示した。  The contaminated soil [soil D] contaminated with dioxins collected from the rubbish incineration site was selected as the contaminated soil of the modified material in this example. The contamination status of dioxins in soil D was determined by measuring the concentration of contained dioxins according to the simple analytical measurement method described in the section of physical property evaluation test method, and the results are shown in Table 54 as pg-TEQ / g concentration.

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なお、以上「注」記載は、以下の分析結果表に共通する。
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The above “Note” is common to the following analysis result tables.

本実施例における改質処理剤としては、参考例2に示した改質処理剤(試料番号A−05)を選んだ。水系溶媒は、河川の水を利用した。改質処理剤によるダイオキシン類を捕捉・分解する一連の作業工程は、汚染土壌100質量部に対して、改質処理剤20質量部と水20質量部の比率で、かき混ぜ混和装置である試験用モルタルミキサー[マイティ30(容量20リッター:攪拌60rpm):(株)愛工舎製作所]を採り、攪拌混和により混和一体化してバサバサで可塑性の混和物とする混和工程に付した。  As the modification treatment agent in this example, the modification treatment agent (sample number A-05) shown in Reference Example 2 was selected. River water was used as the aqueous solvent. A series of work steps for capturing and decomposing dioxins by the modifying treatment agent is for a test mixing device with a mixing ratio of 20 parts by mass of the modifying treatment agent and 20 parts by mass of water with respect to 100 parts by mass of the contaminated soil. A mortar mixer [Mighty 30 (capacity 20 liters: stirring 60 rpm): Aikosha Seisakusho Co., Ltd.] was taken, mixed and integrated by stirring and mixing, and subjected to a mixing step to make a plastic mixture with Basabasa.

次いで該混和物を特別に成型することなく2分割して、それぞれの混和物を2種類の異なる養生工程(常温養生工程もしくは加熱養生工程)に付し、汚染土壌に共存するダイオキシン類の分解・無害化処理を行った。常温養生工程では、混和物を大気中の室温(試験期間中:平均約20℃)に開放して少なくとも7日間放置して、処理土壌の含有水分を5質量%以下まで脱水処理した処理土を常温処理土壌として回収した。加熱養生工程では、混和物を大気中の室温(試験期間中:平均約20℃)に開放して少なくとも3日間放置した時の処理土、さらに100℃に約30分間暴露して脱水処理して処理土の含有水分を脱水処理した処理土を回収した  Next, the mixture is divided into two without special molding, and each mixture is subjected to two different curing processes (room temperature curing process or heat curing process) to decompose dioxins coexisting in the contaminated soil. Detoxification treatment was performed. In the room temperature curing process, the mixture is opened to room temperature in the atmosphere (during the test period: average of about 20 ° C.) and left for at least 7 days, and the treated soil is dehydrated to a moisture content of 5% by mass or less. It collect | recovered as normal temperature processing soil. In the heat curing process, the mixture is opened to room temperature in the atmosphere (during the test period: average of about 20 ° C.) and left for at least 3 days, and then exposed to 100 ° C. for about 30 minutes for dehydration treatment. The treated soil that had been dehydrated was collected.

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ここに回収した3日間放置処理土ならびにさらに加熱脱水した処理土におけるダイオキシン類濃度をそれぞれ物性評価試験方法の項に示した「簡易分析測定法」により分析測定し、3日間放置処理土の場合を表55に、さらに加熱脱水した処理土の場合を表56に表示した。さらに処理土壌Aおよび処理土壌Bにおける簡易型変形性測定試験[q=KN/m]による簡易型変形性、ならびに水溶出pHについて試験を行い、その結果を表57にそれぞれ併せ表示した。The dioxins concentration in the 3-day soil that was collected here and the heat-dehydrated soil was analyzed and measured by the “Simple Analytical Measurement Method” shown in the Physical Properties Evaluation Test Method section. Table 55 shows the case of treated soil that was further heat dehydrated. Furthermore, tests were performed on simple deformability by the simple deformability measurement test [q = KN / m 2 ] and water elution pH in the treated soil A and the treated soil B, and the results are also shown in Table 57.

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以上の結果、ダイオキシン類を含有していた汚染土壌に対して、本発明の改質処理剤と共に水を介した処理・反応を原位置で起動せしめて混和物とし、次いで該混和物を特別な多エネルギーを要する高温での処理をすることなく、含有水分量を限りなくゼロに近づける改質工程に付することにより、汚染土壌に含有するダイオキシン類を捕捉・分解して,環境基準以下に減少されている無公害化物からなる処理土壌に無害化改質されており、ダイオキシン類で汚染されている汚染素材を低コストで、環境に特別な負荷を与えることなく無害化処理されることが良く理解される。  As a result of the above, the contaminated soil containing dioxins was started in-situ with the modifying treatment agent of the present invention in water and made into an admixture. Dioxins contained in contaminated soil are captured and decomposed and reduced to below the environmental standard by subjecting them to a reforming process that keeps the water content as close to zero as possible without processing at high temperatures that require a lot of energy. It has been detoxified and reformed to treated soil made of detoxified substances, and it is often better to detoxify contaminated materials that are contaminated with dioxins at low cost without causing any special environmental impact. Understood.

[実施例19]軟弱地盤
本実施例において、改質処理素材として含水土質である軟弱地盤を選び、該軟弱地盤の原位置で軟弱地盤が含有している含水を介して改質処理剤を活用して、軟弱地盤を強化改質せしめて形状化処理された原位置における形状加工成型品である耐水性の結着形状体について説明する。
[Example 19] Soft ground In this example, a soft ground that is hydrous soil is selected as the reforming treatment material, and the reforming agent is utilized through the moisture contained in the soft ground at the original position of the soft ground. Then, a water-resistant binding shape body which is a shape-processed molded product in the original position where the soft ground is reinforced and reformed and shaped is described.

本実施例で採択した改質処理剤は、参考例2で調製した改質処理剤から試料番号A−14を選び、予め、90kgの水に改質処理剤粉末100kgを分散せしめて調製したスラリー状の改質処理剤を選んだ。本実施例で採択した改質処理素材である含水土質の軟弱地盤としては、茨城県三和町の含水率30質量%の軟弱地盤を選んだ。  The modification treatment agent adopted in this example was a slurry prepared by selecting sample number A-14 from the modification treatment agent prepared in Reference Example 2 and dispersing 100 kg of the modification treatment agent powder in 90 kg of water in advance. The modified treatment agent was selected. As the hydrous soil soft ground which is the modified material adopted in this example, a soft ground with a water content of 30% by mass in Miwa Town, Ibaraki Prefecture was selected.

軟弱地盤原位置における改質補強処理は、土木業界で土壌改良用に汎用されている薬剤注入攪拌方式の深層混合装置により、加圧下に原位置軟弱地盤1mに対して150kgに相当する量の改質処理剤のスラリーを注入攪拌して軟弱地盤地下4mまでの地盤に対してスラリー状改質処理剤を注入攪拌方式で均質混和して混和物とする、次いで原位置で7日間養生後、改質補強地盤の土壌をサンプル採取して物性評価を行った。The reforming and reinforcing treatment at the soft ground in situ is an amount equivalent to 150 kg with respect to 1 m 3 of the in situ soft ground under pressure by a chemical mixing and stirring type deep mixing device that is widely used for soil improvement in the civil engineering industry. The slurry of the modification treatment agent is injected and stirred, and the slurry-like modification treatment agent is homogeneously mixed into the ground up to 4 m below the soft ground by an injection and stirring method to obtain an admixture, and then cured in situ for 7 days. The soil of the modified reinforced ground was sampled and the physical properties were evaluated.

その結果、改質補強処理された軟弱地盤の一軸圧縮強度は、250KN/m以上であり、水溶出pHは9.5以下であった。以上の結果、軟弱地盤にセメントにより有害クロムを持ち込むことなく、本実施例のスラリー状改質処理剤を原位置軟弱地盤に注入攪拌混和することにより、軟弱地盤に補強性を付与する杭が形成されて地盤の補強処理がなされていることが理解される。As a result, the uniaxial compressive strength of the soft ground subjected to the modification reinforcement treatment was 250 KN / m 2 or more, and the water elution pH was 9.5 or less. As a result of the above, without introducing harmful chromium into the soft ground by cement, the slurry-like reforming agent of the present example is injected into the soft ground in the in-situ mixture and mixed to form a pile that gives reinforcement to the soft ground. It is understood that the ground is being reinforced.

[実施例20]一般廃棄物の焼却灰 ダイオキシン類、重金属類
本実施例において、改質処理素材として有害物資であるダイオキシン類、重金属類ならびに水可溶性塩素を共存している一般廃棄物(生ゴミ)の焼却灰を選択し、生ゴミ焼却灰を構成するナトリウム含有成分と活性な生石灰等で調製されている改質処理剤を選び、本発明改質処理方法により形状化処理および無害化処理を施し無公害型の顆粒体に処理調製されている耐水性の結着形状体について説明する。
[Example 20] Incineration ash of general waste Dioxins, heavy metals In this example, general waste (digested garbage) coexisting dioxins, heavy metals, and water-soluble chlorine, which are harmful materials, as reforming materials. ), Select a modification treatment agent prepared with sodium-containing components and active quicklime, etc. constituting the garbage incineration ash, and perform the shaping treatment and detoxification treatment by the present modification treatment method. The water-resistant binder-shaped body that has been treated and prepared into a non-polluted granule will be described.

改質処理素材としては、ダイオキシン類濃度が約2000pg−TEQ/g、鉛含有濃度が530mg/kg、鉛溶出量が0.38mg/Lである参考例1に示した生ゴミ焼却灰(TSW01)を選んだ。改質処理剤としては、生ゴミ焼却灰を構成するナトリウム含有成分を活用して他は試薬より選んだ表58に示した配合で構成される改質処理剤(A−18)を選んだ。水系溶媒は、水道水を選んだ。  As the reforming material, the garbage incineration ash (TSW01) shown in Reference Example 1 having a dioxin concentration of about 2000 pg-TEQ / g, a lead-containing concentration of 530 mg / kg, and a lead elution amount of 0.38 mg / L. I chose. As the modification treatment agent, a modification treatment agent (A-18) constituted by the composition shown in Table 58, which was selected from the reagents, was selected by utilizing the sodium-containing component constituting the garbage incineration ash. Tap water was selected as the aqueous solvent.

本実施例における改質処理方法における顆粒体の改質処理作業工程は、生ゴミ焼却灰100kgに対して、改質処理剤20kgおよび水道水60kgを加えて、回転攪拌軸羽を有した混合機に採り、約10分間混合攪拌しながら混和物としながら2ないし10mmφの粒径からなる顆粒体に成型する混和・加工工程に付し、ここに成型された顆粒体を常温の大気中で28日間養生工程に付する工程により、顆粒体からなる耐水性の結着形状体を処理加工調製した。  In the modification treatment method of the present embodiment, the granule modification treatment work step is performed by adding 20 kg of a modification treatment agent and 60 kg of tap water to 100 kg of garbage incineration ash, and a mixer having a rotating stirring shaft blade The mixture is subjected to an admixing and processing step for forming a granule having a particle diameter of 2 to 10 mmφ while mixing and stirring for about 10 minutes, and the granule thus molded is subjected to 28 days in a normal temperature atmosphere. The water-resistant binding shape body which consists of a granule was processed and prepared by the process attached | subjected to a curing process.

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本実施例で改質処理された顆粒体について、物性評価試験方法の項に準拠して水溶出pH、荷重強度(kg)、水可溶性塩素(mg/kg)、鉛溶出量(mg/L)ならびにダイオキシン類濃度(pg−TEQ/g)をそれぞれ測定して評価した。
これらの結果を表59に併せ表示した。
For the granule modified in this example, water elution pH, load strength (kg), water-soluble chlorine (mg / kg), lead elution amount (mg / L) in accordance with the physical property evaluation test method section In addition, the dioxins concentration (pg-TEQ / g) was measured and evaluated.
These results are also shown in Table 59.

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以上の結果、有害物質を共存している焼却灰を改質処理剤原料として活用し、また改質処理素材として、本発明改質方法により処理調製された焼却灰の顆粒体は、形状化処理されて5kg以上の荷重強度を示し、また無害化処理されて水溶出pHが10未満であり、しかも共存する有害物質がそれぞれ環境基準値をクリヤーしておいり、焼却灰の接着形状体として有効利用できる耐水性の結着形状体であることが良く理解される。  As a result of the above, incineration ash coexisting with harmful substances is used as a raw material for reforming treatment, and as a reforming treatment material, the incinerated ash granules prepared by the present modification method are shaped. It shows a load strength of 5 kg or more, is detoxified and has a water elution pH of less than 10, and coexisting harmful substances clear the environmental standard value, making it effective as an incinerated ash adhesive shape. It is well understood that it is a water-resistant binding shape that can be used.

[実施例21]含水土質 底質の顆粒化
本実施例において、改質処理素材として含水泥土である海域の底質を選択し、底質が含有する含有水を水系溶媒として活用して改質処理剤を加え、本発明の改質処理方法により形状化処理ならびに無害化処理を施して、構造体もしくは顆粒体に加工改質処理されている耐水性の結着形状体について説明する。
[Example 21] Hydrous soil granulation of bottom sediment In this example, the bottom sediment of the marine area that is hydrous mud soil is selected as the reforming treatment material, and the water contained in the bottom sediment is utilized as an aqueous solvent for reforming. A water-resistant binder-shaped body that has been processed and modified into a structure or a granule by adding a treatment agent and performing a shaping treatment and a detoxification treatment by the modification treatment method of the present invention will be described.

改質処理素材としては、海域[英虞湾]から採取した底質[含水比約:158、水分含有量:59.5%、粒度構成:粘土63、シルト24、砂10、礫3%]を選んだ。改質処理剤としては、参考例2に示した中から表60に示した改質処理剤を選んだ。  As a reforming treatment material, sediment collected from the sea area [Ago Bay] [water content ratio: about 158, water content: 59.5%, particle size composition: clay 63, silt 24, sand 10, gravel 3%] I chose. As the modifying agent, the modifying agent shown in Table 60 was selected from those shown in Reference Example 2.

本実施例における底質を改質処理素材とする処理試験体は、物性評価試験方法の項記載の方法に準拠して、表58示す配合割合で、含水比の調整された底質に改質処理剤を加えて含有する海水を水系溶媒として混和一体化して可塑性混和物とした。次いで該混和物を円柱状試験体(構造体)に成型して室温(約25℃)の気中に2ヶ月間放置し、また該混和物を約7mmφ顆粒状試験体(顆粒体)に造粒成型して気中に24時間放置後、海水中に2ヶ月間放置し、底質を構造体もしくは顆粒体とする改質処理剤の改質方法により接着形状体としての提供可能な耐水性の結着形状体に調製した。  The treatment test specimen using the bottom sediment in this example as the reforming treatment material was modified to the bottom sediment adjusted in the water content ratio at the blending ratio shown in Table 58 in accordance with the method described in the physical property evaluation test method. Seawater containing a treatment agent was mixed and integrated as an aqueous solvent to obtain a plastic mixture. Next, the mixture is molded into a cylindrical test body (structure) and left in the air at room temperature (about 25 ° C.) for 2 months. The mixture is formed into an about 7 mmφ granular test body (granule). Water resistance that can be provided as an adhesive shaped body by a modification method of a modification treatment agent that is granulated and left in the air for 24 hours and then left in seawater for 2 months to make the bottom structure or structure. It was prepared in the binding shape.

各円柱状試験体(固化体)および顆粒状試験体(顆粒体)における物性評価は、耐水性、耐熱性、水溶出pH、窒素溶出試験(mg/L)および固化体の一軸圧縮強度試験[KN/m]ならびに顆粒体の荷重強度試験(kg)をそれぞれ測定した。その結果を表59に併せ表示した。なお、顆粒状試験体(顆粒体)においては、2ヶ月間海中養生した顆粒体を室温で48時間乾燥した顆粒体を物性評価用試験体とした。The physical properties of each cylindrical specimen (solidified body) and granular specimen (granules) were evaluated by water resistance, heat resistance, water elution pH, nitrogen elution test (mg / L), and uniaxial compressive strength test of the solidified body [ KN / m 2 ] and the load strength test (kg) of the granules were measured. The results are also shown in Table 59. In addition, in the granular test body (granular body), a granule obtained by drying a granule cured underwater for 2 months at room temperature for 48 hours was used as a test body for evaluating physical properties.

Figure 2006247645
Figure 2006247645

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なお、表62に「水産用水基準」として[水産生物を対象として法的に定められた水質基準はないが、日本水産保護協会刊行が示している水域において望ましい水質基準]として示されている中から全窒素の溶出量を参考までに示す。  In Table 62, “Water quality standards for fisheries products” are listed as [preferred water quality standards in the water areas published by the Japan Fisheries Protection Association, although there is no legally established water quality standard for aquatic products] The elution amount of total nitrogen is shown for reference.

Figure 2006247645
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以上の結果、海域底質を改質処理剤原料として調製した改質処理剤、改質処理素材として選んだ海域の底質に対して、海域底質を改質処理剤原料として調製した改質処理剤も含めた本発明改質処理剤による一連の作業工程でしかも海中における養生工程で加工処理することにより、水溶出pHが10以下の固化体ならびに顆粒体で再泥化しない固化体強度を有していており、接着形状体として利用可能な耐水性の結着形状体が処理調製されていることがよく理解される。特に、底質を改質処理剤原料として調製した改質処理剤により海域底質を改質処理して海水中で養生した顆粒体は、充分な強度が確保されており、本発明改質処理剤により海域底質を再泥化しない状態で形状化処理されて、pH値も低く、海中生態系に悪影響を与えない顆粒体に改質されており、接着形状体として海域海底における覆砂や盛土等の用途に有効に提供できることが良く理解される。  As a result of the above, reforming agents prepared using sea bottom sediments as raw materials for reforming treatments, and reforming materials prepared using sea bottom sediments as raw materials for reforming treatments against the bottom sediments of sea areas selected as reforming raw materials. By processing in a series of work steps with the modified treatment agent of the present invention including the treatment agent and in the curing process in the sea, the solidified body having a water elution pH of 10 or less and the solidified body strength not to be re-mudged with granules are obtained. It is well understood that a water-resistant binding shape that is present and available as an adhesive shape has been processed and prepared. In particular, granules obtained by modifying the bottom sediment of the sea area with a modification treatment agent prepared using the bottom sediment as a raw material for the modification treatment agent and curing in seawater have sufficient strength, and the modification treatment of the present invention. It is shaped into a state that does not re-mudge the seabed sediment with the agent, has a low pH value, and has been modified to granules that do not adversely affect the marine ecosystem. It is well understood that it can be effectively provided for uses such as banking.

[実施例22]顆粒群体集合品を粟オコシ状
本実施例において、各種顆粒状ないし骨材状の顆粒体の集合体である顆粒群体に対して、予め調製された糊状ないしは可塑状の流動性混和物で顆粒群体表面を濡らして異層膜を形成せしめて顆粒体相互を接着せしめ、このとき必要に応じて顆粒群体の集合体に貫通性空隙を有しせしめ、顆粒群体を粟オコシ状に集合一体化せしめた顆粒群体集合品である耐水性の結着形状体について説明する。
[Example 22] Granule group aggregated product is a scalloped shape In this example, a paste-like or plastic flow prepared in advance with respect to a granule group which is an aggregate of various granular or aggregated granules The surface of the granule group is wetted with the adsorbent mixture to form a heterogeneous film, and the granules are adhered to each other. At this time, the aggregate of the granule group is made to have a penetrating void, and the granule group is shaped like a sorghum. The water-resistant bound-shaped body, which is an aggregate product of granule aggregates that are assembled and integrated together, will be described.

本実施例において採択される顆粒群体を構成する顆粒体としては、実施例8ならびに21において本発明改質処理方法により改質処理された不特定形状化品である各顆粒体、さらに既存品である顆粒状・骨材状である粒径が2ないし12mmφで、かさ密度が0.2ないし3.5g/ccの球体、中空体、円柱体、フレーク体、顆粒体を選び、または不特定粒状体の中から2〜8φmmに整粒されているかさ密度が0.5〜0.6(g/cc)の市販パーライト粒[黒曜石を800〜1200℃で急速加熱して体積膨張せしめた軽量無機粒状素材(試料番号FC−08)ならびにガラスカレット(試料番号FC−11)から選んだ。顆粒群体を粟オコシ状集合体に一体化せしめる糊状ないしは可塑状の流動性混和物は、参考例2に示した流動性混和物から選んだ。  As the granules constituting the granule group adopted in this example, each granule, which is an unspecified shaped product modified by the modification treatment method of the present invention in Examples 8 and 21, and further existing products are used. Choose a spherical, hollow, cylindrical, flake, granule with a granular or aggregate particle size of 2-12mmφ and a bulk density of 0.2-3.5g / cc, or unspecified granularity Commercial pearlite grains with a bulk density of 0.5-0.6 (g / cc) that are sized from 2 to 8 mm from the body [lightweight inorganic in which obsidian is rapidly heated at 800-1200 ° C. and volume expanded. It was selected from a granular material (sample number FC-08) and a glass cullet (sample number FC-11). The paste-like or plastic fluid mixture for integrating the granule mass into the cocoon-like aggregate was selected from the fluid mixture shown in Reference Example 2.

選んだ顆粒群体10kgに約5kgの水を加え顆粒体群表面を濡らした後、接着剤である糊状混和物15kgを加え顆粒群体表面全体を被覆して顆粒群体を集合体として一体化せしめ、顆粒体群を厚み30mmで300×300mmの型枠に流し込み成型して常温で少なくとも48時間放置して硬化せしめた後、脱型して粟オコシ状の集合体形状化品である顆粒群体集合品からなる耐水性の結着形状体に調製した。  About 5 kg of water is added to 10 kg of the selected granule group, and the surface of the granule group is wetted. Then, 15 kg of an adhesive paste is added to cover the entire surface of the granule group and the granule group is integrated as an aggregate. The granule group is cast into a 300 × 300 mm mold having a thickness of 30 mm, allowed to stand at room temperature for at least 48 hours and cured, and then demolded to form a granule group aggregate shaped product that is an agglomerated aggregate shaped product. A water-resistant binder shaped body was prepared.

各粟オコシ状の顆粒群体集合品の物性評価を物性評価試験方法の項記載に準拠して、耐水性ならびに耐熱性を確認し、水溶出pHを測定した。また、各粟オコシ状の顆粒群体集合品における貫通性を確認するために、盤状の粟オコシ状顆粒群体集合品に水を落として、粟オコシ状顆粒群体集合品からなる下部に水が流出する方法にて貫通性を確認した。これらの結果を表63に示した。  Based on the description of the physical property evaluation test method, the water resistance and heat resistance were confirmed and the water elution pH was measured. In addition, in order to confirm the penetrability of each cocoon-like granule aggregate assembly, water is dropped on the discoid coconut-like granule aggregate assembly, and water flows into the lower part of the coconut-like granule aggregate assembly. The penetrability was confirmed by this method. These results are shown in Table 63.

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以上の結果、本実施例で処理調製された顆粒群体集合品は、耐水性で耐熱が確保され、pH10未満の低アルカリ性が確保され、必要に応じて貫通空隙を有している粟オコシ状の集合群体からなる顆粒群体集合品であり、無機質で耐水性・耐熱性で通気性、透水性、軽量性、重量性等を有していることから、具体的な用途例としは、各種液体のろ過体、浄化体等に好適なハニカムやキャリヤー等の基材として、また気体の吸着体、触媒体、清浄体、保温材、活性材等として、さらにまた防音壁材、緑化植物等の基材、建材類、土木資材等として有効に利用可能であることが良く理解される。  As a result of the above, the granule aggregate assembly processed and prepared in this example is water-resistant and heat-resistant, has a low alkalinity of less than pH 10, and has a through-hole as necessary. It is an aggregate product of granular aggregates consisting of aggregates, which are inorganic, water-resistant, heat-resistant, breathable, water permeable, lightweight, and heavy. As a base material such as a honeycomb or a carrier suitable for a filter body, a purification body, etc., as a gas adsorbent body, a catalyst body, a cleaning body, a heat insulating material, an active material, etc., and further as a base material for a soundproof wall material, a greening plant, etc. It is well understood that it can be effectively used as building materials and civil engineering materials.

また、調製した粟オコシ状顆粒群体集合品[試料番号21−4]を不燃性防音板として応用したときの防音効果を評価するため、JIS A 1416規格に準拠して防音板としての評価を行うため、不燃性、かさ密度、寸法安定性、圧縮強度、曲げ強度、耐水性ならびに耐候性に関してそれぞれ測定し、その結果を表64に併せ表示した。  In addition, in order to evaluate the soundproofing effect when the prepared coral-like granule aggregate assembly [Sample No. 21-4] is applied as a non-combustible soundproofing plate, it is evaluated as a soundproofing plate in accordance with the JIS A 1416 standard. Therefore, the nonflammability, the bulk density, the dimensional stability, the compressive strength, the bending strength, the water resistance and the weather resistance were measured, and the results are also shown in Table 64.

以上の結果、底質、下水汚泥、焼却灰、パーライト、廃ガラスカレット等からなる顆粒集合群体を本実施例の糊状混和物を接着剤にして一体化せしめて粟オコシ状の顆粒群体集合品とするときは、この粟オコシ状顆粒群体集合品の水溶出pHが10未満で耐水性および耐熱性を有しており、防音効果に優れた不燃性防音板として有効であることがよく理解される。  As a result of the above, granule aggregates consisting of bottom sediment, sewage sludge, incinerated ash, perlite, waste glass cullet, etc. are integrated by using the paste-like admixture of this embodiment as an adhesive, and the aggregates of 粟 okoshi granules It is well understood that the water-elution pH of the aggregate of the sorghum-like granule aggregate is less than 10 and has water resistance and heat resistance, and is effective as a non-combustible soundproof plate with excellent soundproofing effect. The

Figure 2006247645
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[実施例23]注充填一体化品
本実施例において、改質処理素材として選択したガラクタ類の集合群体が収納されている容器に対して、改質処理剤を水系溶媒に分散させたスラリー状改質処理剤を注入充填して容器内でガラクタ類集合群体とスラリー状改質処理剤を混和一体化せしめた一体化品からなる耐水性の結着形状体について説明する
[Example 23] Note-filled integrated product In this example, a slurry in which a modification treatment agent is dispersed in an aqueous solvent in a container in which an aggregate group of galactors selected as a modification treatment material is stored. A description will be given of a water-resistant binder-shaped body composed of an integrated product obtained by injecting and filling a modification treatment agent and mixing and integrating a gang-like aggregate group and a slurry modification treatment agent in a container.

本実施例における改質処理素材であるガラクタ集合群体としては、特殊セメントで内張りされた200Lドラム缶に収納された処理廃棄物の硫酸ナトリウム(芒硝)粉末を30×20×15mmのアーモンド状に加圧成型したタブレット楕円球群からなるガラクタ集合群体を選んだ。本実施例における改質処理剤は参考例2に示した中から選び、また機能付与剤は参考例6ないし7に示したインプルーブメントであるリン酸ケイ素(FI−01)ならびにケイ酸バリウム(FI−07)等から選びスラリー状改質処理剤の作業可使時間ならびに硬化時間の調製可能な改質処理剤を選び予め調製した。  In the present embodiment, the crumb assembly as a modified material is pressed into 30 × 20 × 15 mm almonds of sodium sulfate (sodium nitrate) powder, which is stored in a 200L drum lined with special cement. We chose a jumbled group consisting of molded tablet ellipsoidal spheres. The modification treatment agent in this example is selected from those shown in Reference Example 2, and the function-imparting agents are the silicon phosphate (FI-01) and barium silicate (FI) which are the improvements shown in Reference Examples 6 to 7. -07) etc. were selected in advance to select a modification treatment agent capable of adjusting the working life of the slurry-like modification treatment agent and the curing time.

上記スラリー状の改質処理剤100kgに水道水90kgを加えて分散せしめたスラリー状混和物を選んだ。ここに調製したスラリー状混和物の流動性を一定時間の範囲で粘性として測定して、ガラクタ集合体納容器へのスラリー状混和物を注入する一体化作業続行性の確認を行った。本実施例の流動性混和物の粘性の測定は、30℃に保持された粉状改質処理剤に35℃の水を所定量割合で加えて攪拌し、調製した流動性混和物を52℃の恒温槽中にて養生し、60分後の混和物の粘性をC型粘度計により測定し、結果をCP[センチポイズ]で表65に表示した。  A slurry-like admixture in which 90 kg of tap water was added to 100 kg of the slurry-like modifying treatment agent and dispersed was selected. The fluidity of the slurry-like admixture prepared here was measured as a viscosity within a certain time range, and the continuity of the integrated work for injecting the slurry-like admixture into the garactor assembly container was confirmed. The viscosity of the fluid admixture of this example was measured by adding 35 ° C. water to the powdery reforming agent maintained at 30 ° C. at a predetermined ratio and stirring the prepared fluid admixture at 52 ° C. The viscosity of the mixture after 60 minutes was measured with a C-type viscometer, and the results are shown in Table 65 as CP [centipoise].

なお、本実施例では、容器内で空隙を残すことなく注入一体化を可能とする限界ペースト粘性がスラリー改質処理剤調製10分後のペースト粘性で8000CPを超えない範囲とし、一方作業可能な可使時間を1時間として、その1時間の範囲でペースト粘性が20,000CPを超えない粘性が良好な作業性を確保できる条件とした。  In this example, the limit paste viscosity that enables injection integration without leaving any voids in the container is set so that the paste viscosity after 10 minutes of slurry modification treatment agent preparation does not exceed 8000 CP, and one of the operations is possible. The pot life was set to 1 hour, and the viscosity of the paste not exceeding 20,000 CP in the range of 1 hour was set as a condition for ensuring good workability.

Figure 2006247645
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加圧タブレット化されたアーモンド状芒硝260kgを収納した200Lドラム缶に上記のスラリー化改質処理剤110kgを10分間でドラム缶内に空隙を残さないように注意して注入して充填して一体化物とし、常温に28日間放置養生して注充填されて一体化品に処理調製した。このとき採択したスラリー状改質処理剤を本明細書に示した物性評価試験方法に準拠して円柱状処理試験体を同時に調製し、室温(約25℃)に28日間放置して各円柱状処理試験体とし、調製した円柱状処理試験体における物性評価を耐水性および水溶出pHを測定して評価した。その結果を表66に併せ表示した。  Into a 200L drum can containing 260kg of almond-like salt cake that has been compressed into tablets, 110kg of the above slurrying modifier is poured and filled in 10 minutes so as not to leave a void in the drum can. Then, it was allowed to stand at room temperature for 28 days and poured and filled to prepare an integrated product. At this time, the cylindrically modified test specimens were prepared at the same time in accordance with the physical property evaluation test method shown in this specification, and the slurry-like modifying agent adopted at this time was allowed to stand for 28 days at room temperature (about 25 ° C.). The physical properties of the prepared cylindrical processed specimen were evaluated by measuring water resistance and water elution pH. The results are also shown in Table 66.

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Figure 2006247645

以上の結果、アーモンド状硫酸ナトリムの集合体群で一定の空隙率を有する改質処理素材が収納されたドラム缶容器内に、注入流動性が一定時間確保されたスラリー状改質処理剤を注入充填して一体化品とするとき、アーモンド状硫酸ナトリムの集合群体が飛散することない一体化品からなる耐水性の結着形状体に調製されることが理解される。  As a result of the above, a slurry-like reforming agent with a fixed injection fluidity is injected and filled into a drum container containing a reforming material having a certain porosity in a group of almond-like sodium sulfate aggregates. When an integrated product is obtained, it is understood that the aggregated body of almond-like sodium sulfate is prepared into a water-resistant binding-shaped product made of an integrated product that does not scatter.

本発明によれは、従来の常温施工が可能な水硬性固化材が抱えてきた諸課題を解消して、低コストで汎用性のある水硬性改質処理剤を環境に負荷を与えず製造することが可能であることから、その改質処理剤が有する改質処理機能(無害化機能と形状化機能)活用して、有害物質を共存する廃棄物類等を改質処理素材として省エネ型で再資源化資材として土木資材や一般活用資材等に有効再生利用できる耐水性の結着形状体を提供できることから、特に廃棄物類を取り扱う産業分野での利用・活用の可能性は大きく、さらに環境問題の解消と循環型社会の構築に貢献できる可能性は大きい。  According to the present invention, various problems that have been encountered with conventional hydraulic solidification materials that can be applied at normal temperature are solved, and a low-cost and versatile hydraulic property-modifying treatment agent is produced without giving an environmental load. Because it is possible to utilize the reforming processing function (detoxification function and shaping function) of the reforming agent, wastes that coexist with harmful substances can be used as an energy-saving type reforming material. Since it is possible to provide water-resistant binders that can be effectively recycled and reused for civil engineering materials and general use materials as recycling materials, there is a great potential for use and utilization in industrial fields that handle waste in particular. There is great potential for solving problems and building a recycling-oriented society.

生活環境において処理・処分の必要性が求められる代表的な廃棄物類である含水底質類、下水汚泥ケーキ、焼却灰、汚染土壌・農地、軟弱地盤、ガラクタ状廃棄物類等を改質処理素材として、環境に特別な負荷を与えず低コストで安全に処理・処分が可能である本発明の一連の作業工程からなる簡単な改質処理方法により改質処理して再生利用可能な再資源化資材として提供できる代表的な本発明接着形状体について、下記にその概要を記載する。  Remediate treatment of water-containing sediments, sewage sludge cake, incinerated ash, contaminated soil / farmland, soft ground, junk waste, etc., which are typical wastes that need to be treated and disposed of in the living environment As a material, it can be recycled and recycled by a simple reforming method consisting of a series of work processes according to the present invention that can be safely processed and disposed of at low cost without giving a special load to the environment. The outline of a typical bonded shape body of the present invention that can be provided as a chemical material is described below.

1.含水底質類の再資源化処理の場合、
閉鎖性海域、河川、湖沼、ダム等の水域底部にある底質は、今日の環境状況から重金属類ならびにダイオキシン類を共存しており、しかも貧酸素化と共に有害物質により生態系ならびに環境への影響は甚だしく大きく底質の処理・処分には窮している。しかし、本発明改質処理材を活用する改質処理方法によれば、水域底部の浚渫底質に含水比を好適には150以下に脱水調整し、乾燥物基準で100質量部に相当する含水底質に対して、本発明改質処理材を10ないしは30質量部を加えて混和して混和物とする。
1. In the case of recycling of hydrous sediments,
The sediments at the bottom of closed waters such as closed seas, rivers, lakes, and dams coexist with heavy metals and dioxins due to today's environmental conditions, and also have an impact on ecosystems and the environment due to toxic substances along with hypoxia. Is very large and hesitate to treat and dispose of sediment. However, according to the reforming method using the reforming material of the present invention, the moisture content of the dredged sediment at the bottom of the water area is preferably adjusted to dehydration to 150 or less, and the content corresponding to 100 parts by mass on the dry matter basis is included. 10 to 30 parts by mass of the modified material of the present invention is added to the bottom sediment and mixed to obtain an admixture.

次いで顆粒物等に形状化した形状化物を大気中ないしは水中に開放放置して養生するときは、少なくとも7日後には、pH値10未満で共存する重金属類は固定・不溶化されており、共存していたダイオキシン類は分解されて無害化されており、一軸圧縮強度で500KN/m以上が確保された形状化品が形成されており、貧酸素状態を作らず再泥化しない顆粒品(用途:漁礁、底部形成材、盛土材、中込材、覆砂材、造成材、築堤材、植栽用土材等)からなる無公害型接着形状体として提供することができる。Next, when the shaped product formed into granules or the like is left open and cured in the air or water, the heavy metals coexisting at a pH value of less than 10 are fixed and insolubilized at least after 7 days. Dioxins are decomposed and detoxified, and formed into a shaped product with a uniaxial compressive strength of 500 KN / m 2 or more, which does not create an anoxic state and does not re-mudder (use: It can be provided as a pollution-free adhesive shape body made of a reef, a bottom forming material, an embankment material, an intermediate material, a sand covering material, a building material, a banking material, a planting soil material, or the like.

2.下水汚泥ケーキの緑化資材化処理の場合
日々大量に発生している下水汚泥や農業集落排水汚泥等の有害物質を共存している汚泥類は、脱水汚泥、乾燥汚泥、炭化汚泥、焼却灰、コンポスト、溶融スラグ等に処理して、緑農地利用、建設資材利用、燃料化、海洋還元、埋立処分等で処理されている。しかるにこれら汚泥の処分にはいずれも高価で特別な設備を必要とし、さらに多エネルギーを必要としており、処理・処分に高コストの負担が強いられている。
2. When processing sewage sludge cakes into greening materials Sludges that coexist with toxic substances such as sewage sludge and agricultural village drainage sludge that are generated daily are dehydrated sludge, dried sludge, carbonized sludge, incinerated ash, compost It is processed into molten slag, etc., and used for green farmland use, construction material use, fuel conversion, ocean reduction, landfill disposal, etc. However, disposal of these sludges is expensive and requires special equipment, and also requires a lot of energy, and a high cost burden is imposed on treatment and disposal.

しかし、本発明改質処理方法を活用すれば、まず含水汚泥に水担持の能力を有する焼却灰等を加えて含水量を調整しつつ本発明の改質処理材を加えて、含水汚泥を構成する休眠成分を活用して、共存重金属類を固定・不溶化し、悪臭を消臭化して無害化処理し、必要に応じてその他の有機質資材や有機質廃棄物を加えてコンポスト化して粉粒体ないしは顆粒体からなる再資源化資材として、植栽用土材、緑化基盤材、芝目土材、土壌改良・改質材等に安価にして有効に提供することができる。  However, if the modified treatment method of the present invention is utilized, the modified sludge is added to the hydrated sludge by first adding incinerated ash having the ability to carry water to adjust the moisture content, thereby forming the hydrated sludge. By using the dormant component, the coexisting heavy metals are fixed and insolubilized, deodorized and deodorized by deodorizing, and if necessary, other organic materials and organic waste are added to compost and granulate or As recyclable materials made of granules, it can be effectively provided at low cost for soil for planting, greening base material, lawn earth material, soil improvement / modification material, and the like.

3.有害物質共存焼却灰の常温無害化処理の場合
一般廃棄物・産業廃棄物や汚泥の焼却灰、ならびに火力発電所より排出されるフライアッシュ類の灰類は、有害物質である重金属類ならびにダイオキシン類を共存しており、一般には一部であるが高価な設備により1400℃で溶融スラグに処理して土木資材代替品として、またセメント用副原料として一部再利用されている。しかし、大半は、管理区域に埋立処分されている。しかし、現在埋立処分地は急速に減少しており、延命策も講じられているが抜本的解決策がない状況にある。
3. In case of detoxification treatment of toxic substance coexisting incineration ash Incineration ash of general waste / industrial waste and sludge and fly ash ash discharged from thermal power plants are hazardous heavy metals and dioxins In general, it is partly reused as a substitute for civil engineering materials by treating it with molten slag at 1400 ° C. with some expensive equipment, and as a secondary material for cement. However, most are landfilled in controlled areas. However, the number of landfill sites is decreasing rapidly, and life-prolonging measures have been taken, but there is no drastic solution.

しかし、本発明改質処理方法を活用すれば、まず焼却灰を構成する休眠成分を活用する自己完結型の改質処理手段により、共存する有害物質群を無害化処理し、同時に形状化処理してpH値10未満の例えば顆粒体もしくは構造体(用途:盛土材、中込材、覆砂材、造成材、築堤材、植栽用土材等)からなる無公害型の再資源化土木資材として提供することができる。  However, if the reforming treatment method of the present invention is utilized, first, the coexisting harmful substance group is detoxified by the self-contained reforming processing means utilizing the dormant component constituting the incinerated ash, and simultaneously shaped. Provided as non-polluting, recyclable civil engineering materials consisting of, for example, granules or structures having a pH value of less than 10 (uses: embankment materials, insert materials, sand covering materials, construction materials, embankment materials, planting earth materials, etc.) can do.

4.汚染土壌・農地の原位置修復処理の場合
工場等の跡地における汚染地盤や農地からなる汚染土壌には、有害な重金属類ならびにダイオキシン類を共存している場合があり、汚染土壌対策法から、これら汚染土壌を利用しようとするときは、これら有害物質の含有量が一定の環境基準値以下であることが法的に規制されており、汚染土壌では有害物質を環境基準値以下にしてから土地利用することが定められている。
4). In-situ restoration of contaminated soil and farmland Contaminated soil and farmland in contaminated soil and farmland in factory sites may coexist with harmful heavy metals and dioxins. When using contaminated soil, it is legally regulated that the content of these hazardous substances is below a certain environmental standard value. It is stipulated to do.

しかし、本発明改質処理方法を活用すれば、原位置に存在する汚染土壌を乾燥物基準で100質量部に対して、必要に応じて処理対象地盤における土壌の含有水分が30質量%以上になるように水を加え、本発明改質処理材を10ないし30質量部を加えて原位置で混和し、混和現場における環境大気中に放置して養生するときは、少なくとも7日後には、共存していた重金属類は固定・不溶化されており、共存していたダイオキシン類が分解されて無害化されており、土壌地盤もしくは農地として活用できる状態に改質処理されて無公害型に修復処理された壌地盤もしくは農地を提供することができる。  However, if the modified treatment method of the present invention is used, the soil content in the soil to be treated is 30% by mass or more if necessary, with respect to 100 parts by mass of the contaminated soil existing on the dry matter basis. When water is added, and 10 to 30 parts by mass of the modified material of the present invention is added and mixed in-situ, and left in the ambient atmosphere at the mixing site for curing, at least after 7 days, coexistence The heavy metals that were used were fixed and insolubilized, and the coexisting dioxins were decomposed and detoxified, modified to a state that can be used as soil ground or agricultural land, and restored to pollution-free type Can provide the soil or farmland.

5.軟弱地盤の環境に負荷を与えない補強改質処理の場合
埋立地や本来軟弱な地盤に一定強度を確保して活用しようとするときは、従来セメントを改質処理剤として地盤改良が行われてきたが、セメントが有するアルカリや含有クロムによる環境への二次公害汚染が問題となり、問題となっている。
5. In the case of reinforcement and reforming treatment that does not place a burden on the environment of soft ground When attempting to secure a certain level of strength in landfills or inherently soft ground, conventional ground improvement has been carried out using cement as a modification treatment agent. However, secondary pollution to the environment due to the alkali and chromium contained in the cement has become a problem.

本発明改質処理方法を活用すれば、埋立地や軟弱な地盤の存在する原位置において、埋立地や軟弱な地盤土壌の乾燥物基準で100質量部に相当する処理対象とする地盤土壌に対して、必要に応じて処理対象地盤における含有水分量が30質量%以上になるよう水を加え、本発明改質処理材を10ないし30質量部を加えて均質混和した混和物を混和・成型した状態で原位置現場の大気環境中に放置・養生するときは、少なくとも7日後には、一軸圧縮強度で1000KN/m以上が確保され、共存重金属類は固定・不溶化されており、共存ダイオキシン類が分解・無害化され、土地活用のできる地盤状態に改質処理することができる。By utilizing the modified treatment method of the present invention, in the original position where there is a landfill or soft ground, with respect to the ground soil to be treated corresponding to 100 parts by mass on the dry matter basis of the landfill or soft ground soil Then, if necessary, water is added so that the water content in the ground to be treated is 30% by mass or more, and 10 to 30 parts by mass of the modified material of the present invention is added to mix and mold the mixture. When left standing and cured in the atmospheric environment at the site in situ, at least 7 days later, a uniaxial compressive strength of 1000 KN / m 2 or more is secured, and the coexisting heavy metals are fixed and insolubilized. Can be decomposed and detoxified, and reformed to a ground state that can be used for land.

6.吸着性多孔質体の吸着性を生かした顆粒化処理の場合
従来技術において、吸着性多孔質細孔を有する無機質の粉粒状の吸着体である活性炭等の炭素体、比表面積の大きいシリカ・アルミナ等ゲル体、ゼオライト等の粉粒状吸着体を取り扱い容易な粒状ないしは顆粒状に成型しようとするときに、有機質バインダーを採択するのでは粉粒状吸着体が有していた細孔や比表面積が潰され、吸着体の特性である吸着性が生かされない。
6). In the case of granulation treatment making use of the adsorptivity of the adsorptive porous material In the prior art, carbon bodies such as activated carbon, which is an inorganic powder-like adsorbent having adsorptive porous pores, silica / alumina having a large specific surface area When an organic binder is used when trying to form a granular adsorbent such as an isogel body or zeolite into an easily handled granular or granular form, the pores and specific surface area of the granular adsorbent are crushed. Therefore, the adsorptivity that is a characteristic of the adsorbent is not utilized.

本発明改質処理方法を活用すれば、比表面積25m/g以上である吸着性多孔質細孔を有する粉粒状吸着体を処理対象素材として、粉粒体の吸着性多孔質の細孔を生かして、吸着性の多孔質性細孔を殺すことなく細孔を確保して、吸着性を有する粉粒体の固結体、例えば取り扱いやすい顆粒体や成形体・構造体である結着形状体を提供することができる。By utilizing the modified treatment method of the present invention, a granular adsorbent having an adsorbing porous pore having a specific surface area of 25 m 2 / g or more is used as a material to be treated, and the adsorbing porous pore of the granular material is formed. Making use of the adsorbent porous pores without losing the pores, ensuring the pores and adsorbing powder solids, for example, easy-to-handle granules, compacts and structures The body can be provided.

特に、固結処理された形状加工成型品においても吸着性多孔質細孔を確保するためには、処理対象物である吸着性多孔質性細孔を有する粉粒体に対して、予め充分な水を吸着性多孔質性細孔に含浸させて細孔中の空隙を水で充満しておいてから本発明処理材を加えた均質混和せしめ、本発明改質処理材が有する改質処理機能を発揮させた無害化処理すると主に、固結かせしめて形状化処理することが可能であり形状化処理品に吸着性多孔質性細孔を確保することができることから好ましい。  In particular, in order to ensure the adsorptive porous pores even in the shape-processed molded product that has been subjected to the consolidation treatment, it is sufficient in advance for the granular material having the adsorptive porous pores to be processed. Impregnating porous pores with water and filling the voids in the pores with water, and then homogeneously mixing with the treatment material of the present invention, the modification treatment function of the present modification treatment material The detoxification treatment that exhibits the above is mainly preferred because it can be consolidated and shaped, and adsorbable porous pores can be secured in the shaped product.

7.ガラクタ廃棄物類の注入一体化処理の場合
低レベルではあるが放射性廃棄物、医療関係廃棄物類、化学変化の激しい廃棄物類ないしは悪臭を伴う廃棄物類からなるガラクタ類の集合群体等は、単に投棄ないしは埋立てることは禁止されており、所定の条件下で一体化されて管理・保管されることが義務付けられている。
7). In the case of galactor waste infusion and integrated processing, the collective group of galacta composed of radioactive waste, medical-related waste, waste with a strong chemical change or waste with bad odor, etc. It is prohibited to simply dump or landfill, and it is required to be integrated and managed and stored under specified conditions.

本発明改質処理方法を活用すれば、各種の廃棄物類からなるガラクタ類の集合群体が収納されている容器に対して、予め調製された改質処理剤を水系溶媒に分散させたスラリー状改質処理剤を容器内に収納されているガラクタ類集合群体に注入充填してスラリー状改質処理剤と一体化した一体化品からなる結着形状体を提供することができる。  If the modification treatment method of the present invention is utilized, a slurry in which a modification treatment agent prepared in advance is dispersed in an aqueous solvent for a container in which a collection group of galactors composed of various wastes is stored. It is possible to provide a binder-shaped body made of an integrated product in which the modifying treatment agent is injected and filled into a gang-like aggregate group housed in a container and integrated with the slurry-like modifying treatment agent.

Claims (40)

熱履歴シリケートを改質対象素材として、少なくとも常温で水系溶媒を介して活性化し、無害化処理および形状化処理を施す改質処理機能を発揮して無公害型の結着形状体に改質処理する機能を有する改質処理剤において;
上記の熱履歴シリケートが、乾燥物の酸化物基準で表してシリカ成分を20ないしは80質量%、アルミナ成分を5ないしは35質量%、およびカルシヤ成分を1ないしは40質量%を含有して熱履歴を受けている不活性な休眠成分のケイ酸塩系化合物で構成される人工合成品、ゴミ・廃棄物・汚泥の焼却灰、窯業関連廃材・資材もしくは火山噴出物からなる粉粒体であり;
上記水系溶媒が、自然水、人工処理水、排水類ないしは包含水の群より選ばれる単独ないし2種以上の組み合わせの水系液体であり;
上記の改質処理剤が、乾燥物における有効成分換算で表してカルシヤ含有成分に含まれるカルシヤ100質量部に対して、ナトリウム含有成分に含まれる酸化ナトリウムを0.1ないしは5質量部ならびに硫黄含有成分に含まれる硫黄を酸化物換算で1ないしは50質量部の酸化物基準で表した配合割合で3者成分がワンパック粉粒体を構成しており、該ワンパック粉粒体の水サスペンジョンpHが12を超えるアルカリ性であることを特徴とする改質処理剤。
Using heat history silicate as a material to be reformed, it is activated at least at room temperature via an aqueous solvent, and exhibits a reforming treatment function that performs detoxification treatment and shaping treatment. In the modifying agent having the function of:
The above-mentioned heat history silicate contains 20 to 80% by mass of silica component, 5 to 35% by mass of alumina component, and 1 to 40% by mass of calcium component, expressed on the basis of oxide of the dried product. Artificial synthetic products composed of inactive dormant silicate compounds, incineration ash of waste, waste, sludge, ceramics-related waste materials / materials or powders of volcanic products;
The aqueous solvent is a single or a combination of two or more aqueous liquids selected from the group of natural water, artificially treated water, wastewater or inclusion water;
The above-mentioned modifying treatment agent is 0.1 to 5 parts by mass of sodium oxide contained in the sodium-containing component and sulfur-containing with respect to 100 parts by mass of the calcium contained in the calcium-containing component expressed in terms of active ingredients in the dried product. The three-component component constitutes a one-pack powder at a blending ratio in which sulfur contained in the component is expressed in terms of oxide in terms of oxide of 1 to 50 parts by mass, and the water suspension pH of the one-pack powder Is an alkaline agent exceeding 12;
人工合成品
前記の熱履歴シリケートである人工合成品の粉粒体が、ケイ酸塩組成物、カルシヤ組成物ならびにアルミナ組成物の群より選ばれる単独ないし2種以上の組み合わせからなる混合原料で予め調製されており、該混合原料が主成分として乾燥物の酸化物基準で表してシリカ100質量部に対して、カルシヤ30ないし350質量部ならびにアルミナを10ないし150質量部、必要に応じて酸化ナトリウムを1ないし50質量部の範囲で構成されており、該混合原料を820ないし1500℃の範囲で少なくとも15分間熱処理し、次いで回収された熱処理物を80メッシュ、好むらくは150メッシュ篩通過の微粒子に粉砕・分級して調製されている請求項1記載の改質処理剤。
Artificial Synthetic Artificial Synthetic Powder Granule, which is the heat history silicate, is previously mixed with a raw material consisting of a single or a combination of two or more selected from the group of silicate composition, calcium composition and alumina composition. 30 to 350 parts by weight of calcium oxide and 10 to 150 parts by weight of alumina, if necessary, sodium oxide, based on 100 parts by weight of silica expressed as oxides of the dried product as a main component. 1 to 50 parts by mass, the mixed raw material is heat-treated at 820 to 1500 ° C. for at least 15 minutes, and the recovered heat-treated product is then passed through 80 mesh, preferably 150 mesh. The modifying treatment agent according to claim 1, which is prepared by pulverization and classification.
含水体
前記の熱履歴シリケートである人工合成品、ゴミ・廃棄物・汚泥の焼却灰、窯業関連廃材・資材もしくは火山噴出物からなる粉粒体を乾燥物基準で100質量部に対して水が140質量部以下の量割合で包含担持されている粉粒体の含水体、ないしはヘドロ・底質・汚泥処理ケーキの含水泥土もしくは湿潤状態にある粘土・土壌類の土質土で固形分100質量部に対して水が140質量部以下の量割合で包含している含水体である請求項1ないし2記載の改質処理剤。
Water-containing body Artificial synthetic products that are the above-mentioned thermal history silicate, incineration ash of garbage, waste, sludge, ceramics-related waste materials / materials, or powders of volcanic products, water is added to 100 parts by mass on a dry matter basis. 100 parts by mass of solid content in a hydrous body of powder that is included and supported in an amount ratio of 140 parts by mass or less, or a hydrous mud of sludge, bottom sediment, sludge-treated cake, or clay soil in a wet state The modification treatment agent according to claim 1 or 2, which is a hydrous material containing water in an amount of 140 parts by mass or less based on the water content.
有害化学物質
上記の熱履歴シリケートが、原位置または持込位置に存在して、土壌汚染の環境基準項目で示されるカドミニウム、砒素、水銀、鉛、クロム、セレン、ホウ素ないしはフッ素の群より選ばれる単独ないし2種以上の組み合わせの水溶出有害元素群、アルカリ金属元素群、窒素の化合物類ないしはダイオキシン類の単独ないし2種以上の組み合わせの有害化学物質が環境基準を超える範囲で共存している粉粒体ないしは含水体である請求項1ないし3のいずれか1項記載の改質処理剤。
Hazardous chemicals The above heat history silicate is selected from the group of cadmium, arsenic, mercury, lead, chromium, selenium, boron, or fluorine that exists in the original or carry-in position and is indicated in the environmental standards for soil contamination. Powder in which a single or a combination of two or more kinds of water-eluting harmful elements, alkali metal elements, nitrogen compounds or dioxins alone or a combination of two or more harmful chemicals coexist in a range that exceeds environmental standards The modifying agent according to any one of claims 1 to 3, which is a granule or a hydrous material.
自然水、人工処理水、排水類ないしは包含水
前記の水系溶媒が、雨水、河川・湖沼水・たまり水、湧き水、井戸水、海水、人工池・ダム水である自然水;飲料水、工場用水、農業用水、水道水、下水道処理水、産業界の副生水である人工処理水;産業界の排水、生活排水、各種の処理水である排水類;含水土質、底質、土壌地盤、産業廃棄物類、改質対象素材、改質処理剤の包含水の群より選ばれる単独ないし2種以上の組み合わせ水系液体である請求項1ないし4のいずれが1項記載の改質処理剤。
Natural water, artificially treated water, drainage or inclusion water Natural water such as rainwater, river, lake water, pool water, spring water, well water, seawater, artificial pond / dam water; drinking water, factory water, Agricultural water, tap water, sewage treated water, artificial treated water that is by-product water of industry; wastewater that is industrial wastewater, domestic wastewater, various treated water; hydrous soil, bottom sediment, soil ground, industrial waste The reforming agent according to any one of claims 1 to 4, which is a single or two or more combined aqueous liquids selected from the group of substances, material to be reformed, and water included in the modifying agent.
前記改質処理剤を構成するカルシヤ含有成分が、酸化物基準で表して有効成分であるカルシヤを少なくとも25質量%含有しているカルシヤ含有の化合物ないしは組成物からなる粉粒体である請求項1記載の改質処理剤。  2. The calcium-containing component constituting the modification treatment agent is a powder or a granule comprising a calcium-containing compound or composition containing at least 25% by mass of an active ingredient calcium expressed on an oxide basis. The modifying agent as described. 前記改質処理剤を構成するカルシヤ含有成分が、処理石灰を包含する焼却灰類、高炉・製鋼スラグ類、ケイカル廃材、セメント類、ないし廃棄・副生石こうないしはカルシウム塩化合物類の群より選ばれる単独ないし2種以上の組み合わせの休眠成分からなる熱履歴シリケートに共存して有効成分であるカルシウム成分を酸化物基準で表して少なくとも20質量%の量で確保されている含カルシウム休眠成分であり、このとき併配合されるナトリウム含有成分が、活性な水酸化ナトリウムの組み合わせからなる粉粒体ないしは含水体である請求項1記載の改質処理剤。  The calcium-containing component constituting the modifying treatment agent is selected from the group of incinerated ash containing treated lime, blast furnace / steel slag, calcium waste, cement, waste / byproduct gypsum or calcium salt compounds A calcium-containing dormant component that is ensured in an amount of at least 20% by mass of the calcium component that is an active ingredient coexisting with a heat history silicate composed of a single or two or more combinations of dormant components; 2. The modifying agent according to claim 1, wherein the sodium-containing component to be blended at this time is a powder or a hydrated body composed of a combination of active sodium hydroxide. 前記改質処理剤を構成するナトリウム含有成分が、酸化物基準で表して有効成分である酸化ナトリウムを少なくとも2質量%含有しているナトリウム含有の化合物ないしは組成物からなる粉粒体である請求項1記載の改質処理剤。  The sodium-containing component constituting the modifying treatment agent is a powder comprising a sodium-containing compound or composition containing at least 2% by mass of sodium oxide as an active ingredient expressed on an oxide basis. The modifying treatment agent according to 1. 前記改質処理剤を構成するナトリウム含有成分が、下記組成式(1)
Figure 2006247645
[式中:Mはナトリウムないしカリウム元素、aは0.1ないし4の数、wは16ないし50の数]で表されるケイ酸アルカリの群より選ばれる単独ないし2種以上の組み合わせの液状ケイ酸アルカリからなる含水体である請求項1記載の改質処理剤。
The sodium-containing component constituting the modifying agent is the following composition formula (1)
Figure 2006247645
[Wherein, M is an element of sodium or potassium, a is a number of 0.1 to 4, and w is a number of 16 to 50] alone or in combination of two or more kinds selected from the group of alkali silicates The modification treatment agent according to claim 1, wherein the modification treatment agent is a hydrated body made of alkali silicate.
前記改質処理剤を構成するナトリウム含有成分が、ゴミ焼却灰、汚泥焼却灰、赤泥ないしは芒硝類廃液の回収物の群より選ばれる単独ないし2種以上の組み合わせの休眠成分からなる熱履歴シリケートに共存して有効成分であるナトリウム成分を酸化物基準で表して少なくとも1.5質量%含有する含ナトリウム休眠成分であり、このとき併配合されるカルシヤ含有成分が、活性な酸化カルシウムないし水酸化カルシウムの組み合わせからなる粉粒体ないし含水体である請求項1記載の改質処理剤。  Thermal history silicate, wherein the sodium-containing component constituting the modifying treatment agent is a single or a combination of two or more dormant components selected from the group of waste incineration ash, sludge incineration ash, red mud or saltwater waste liquids Is a sodium-containing dormant component containing at least 1.5% by mass of an active ingredient sodium component on an oxide basis, and the calcium-containing component added at this time is active calcium oxide or hydroxylated The modification treatment agent according to claim 1, which is a granular material or a hydrous material comprising a combination of calcium. 前記改質処理剤を構成する硫黄含有成分が、無水物の硫黄分基準で表して有効成分である硫黄分を少なくとも18質量%含有している硫黄のオキシ酸化合物ないし硫化物からなる粉粒体である請求項1記載の改質処理剤。  Granules comprising a sulfur oxyacid compound or a sulfide containing at least 18% by mass of the sulfur component which is an active component when the sulfur-containing component constituting the modifying treatment agent is represented on the basis of the sulfur content of the anhydride The modifying agent according to claim 1, wherein 請求項1ないしは11のいずれか1項記載の改質処理剤を活用して、必要に応じて機能付与剤を付加して少なくとも常温で水系溶媒を介して、改質対象素材となる休眠成分からなる熱履歴シリケートに加えて活性化混和物とする混和工程、必要に応じて該活性化混和物を形状化処理物とする加工工程、次いで該活性化混和物ないし該形状化処理物を所定雰囲気中に開放せしめて結着形状体とする養生工程で構成される一連の作業工程からなる改質処理方法において;
上記の機能付与剤が、サプリメント、インプルーブメント、ファンクショメントもしくはレインホースメントの単独ないし2種以上の組み合わせの粒径500μ以下の粉粒体で構成されており;
上記の混和工程が、原位置または持込位置に存在する熱履歴シリケートを乾燥物基準で100質量部に対して、改質処理剤を乾燥物基準で2ないし20質量部未満を加え、必要に応じて機能付与剤を400質量部以下の量で付加して混和して活性化混和物とし、該活性化混和物中の含有水分の含水率が10ないし70質量%範囲に確保される状態になるように必要に応じて水系溶媒を加えて量割合を調整して混和し、該活性化混和物が常温にて混和・放置される3時間の間のpH値が12を超える状態が確保されてバサバサ状、可塑状、マヨネーズ状、糊状ないしはスラリー状に調製される工程であり;
上記の加工工程が、必要に応じて該活性化混和物を原位置非成型物、耐水性粉粒体物ないしは形状加工成型物からなる形状化処理物とする工程であり;
上記の養生工程が、該活性化混和物ないしは該形状化処理物を常温から100℃範囲にある常圧、加圧、減圧条件下における気中、水中、海中、土中、溶液中、蒸気中、非酸素ガス中の雰囲気の群より選ばれる単独雰囲気中ないし2種以上の組み合わせの多段雰囲気中に少なくとも15分間解放して反応・養生を進行せしめて結着硬化の完了している自己完結型の原位置非成型品、耐水性粉粒体品ないしは形状加工成型品からなる結着形状体とする工程であり;
上記の改質処理方法が、熱履歴シリケートを改質対象素材として、上記の一連の作業工程に付して調製される活性化混和物のアルカリ性成分を固定化してpH10未満が確保され、該改質対象素材に有害物質が共存するときは該有害物質を固定・不溶化する無害化処理を施し、同時に粉粒体熱履歴シリケートを耐水性で水中再泥化しない形状化処理を施して自己完結型の結着形状体に改質処理することを特徴とする改質処理方法。
The modification treatment agent according to any one of claims 1 to 11 is utilized, and a function-imparting agent is added as necessary, and at least at room temperature, through a water-based solvent, from a dormant component serving as a material to be modified. In addition to the thermal history silicate, an admixing step for making an activated admixture, a processing step for making the activated admixture a shaped treatment as necessary, and then the activated admixture or the shaped treated product in a predetermined atmosphere In a reforming method comprising a series of work steps composed of a curing step that is opened inside to form a bound-shaped body;
The above-mentioned function-imparting agent is composed of a granular material having a particle size of 500 μm or less, which is a supplement, improvement, function or rain reinforcement alone or in combination of two or more thereof;
The above mixing step is performed by adding 2 to less than 20 parts by mass of the modification treatment agent with respect to 100 parts by mass of the heat history silicate present in the original position or the carry-in position on the basis of dry substance. Accordingly, a function-imparting agent is added and mixed in an amount of 400 parts by mass or less to make an activated admixture, and the moisture content of the water content in the activated admixture is ensured in the range of 10 to 70 mass%. As necessary, an aqueous solvent is added and the amount is adjusted and mixed to ensure that the activated admixture is mixed and allowed to stand at room temperature for a pH value exceeding 12 for 3 hours. A process that is prepared in the form of rust, plastic, mayonnaise, paste or slurry;
The above-mentioned processing step is a step of making the activated admixture a shaped processed product made of an in-situ non-molded product, a water-resistant granular material or a shaped processed molded product, if necessary;
In the curing process described above, the activated admixture or the shaped product is subjected to normal pressure, pressurization, and decompression under normal pressure, pressurization, and decompression conditions in air, water, sea, soil, solution, and steam. A self-contained type in which the binding and curing are completed by allowing the reaction and curing to proceed for at least 15 minutes in a single atmosphere selected from the group of non-oxygen gas atmospheres or in a multistage atmosphere of a combination of two or more. In-situ non-molded product, water-resistant granular product or shape-processed molded product to form a bound shape;
The above reforming treatment method fixes the alkaline component of the activated admixture prepared by applying the heat history silicate as a material to be modified to the above-described series of work steps to secure a pH of less than 10, When harmful substances coexist in the target material, the detoxification treatment to fix and insolubilize the harmful substances is performed, and at the same time, the granule thermal history silicate is water-resistant and shaped to prevent re-mudging in water. A reforming method characterized by subjecting the binder shaped body to a reforming process.
前記の機能付与剤であるサプリメントが、アルカリ金属塩ないしはアルカリ土類金属塩の化合物を主成分とするアルカリ補充組成物、硫黄のオキシ酸化合物ないしは硫化物を主成分とする硫黄含有組成物、2価ないしは3価の鉄化合物である鉄塩補充組成物、親油性で活性なフェロケイ酸塩組成物もしくはシラノール基含有組成物であるケイ酸塩補充組成物の群より選ばれる単独ないし2種以上の組み合わせの改質処理剤を補充する化合物ないしは組成物からなる粉粒体である請求項13記載の改質処理方法。  The supplement as the function-imparting agent is an alkali replenishing composition mainly comprising a compound of an alkali metal salt or alkaline earth metal salt, a sulfur-containing composition mainly comprising a sulfur oxyacid compound or sulfide, 2 Single or two or more selected from the group consisting of iron salt supplement compositions that are trivalent or trivalent iron compounds, lipophilic and active ferrosilicate compositions, or silicate supplement compositions that are silanol group-containing compositions 14. The modification treatment method according to claim 13, wherein the modification treatment method is a powder or a granule comprising a compound or a composition supplementing the combination modification treatment agent. 前記の機能付与剤であるインプルーブメントが、改質処理機能を改善するリン酸根組成物、改質処理時の作業性を改善するバリウム塩組成物もしくは改質処理作用を向上せしめる分散媒質組成物の群より選ばれる単独ないし2種以上の組み合わせの改質処理剤が有する改質処理の機能性ないしは作業性を改善する化合物ないしは組成物からなる粉粒体である請求項13記載の改質処理方法。  The improvement, which is the above-mentioned function-imparting agent, is a phosphate group composition that improves the modification treatment function, a barium salt composition that improves workability during the modification treatment, or a dispersion medium composition that improves the modification treatment action. 14. The modification treatment method according to claim 13, wherein the modification treatment method comprises a compound or composition that improves the functionality or workability of the modification treatment of a modification treatment agent selected from the group alone or in combination of two or more kinds. . 前記の機能付与剤であるファンクショメントが、形成される水不溶性鉱物を成長させる結晶タネ組成物、結着形状体に緩衝性を付与する緩衝帯形成組成物、各種の機能性液状素材を担持する担持吸着組成物、熱に耐える耐熱火組成物、熱遮断性ないしは保温性を発揮する断熱・保温組成物、固−液分離を促進する沈殿凝集組成物もしくは各種の機能性を付与する機能付与組成物の群より選ばれる単独ないし2種以上の組み合わせの改質処理される結着形状体の物性もしくは機能性を改良・改善する化合物ないしは組成物からなる粉粒体である請求項13記載の改質処理方法。  The function as a function-imparting agent carries a crystal seed composition for growing a water-insoluble mineral to be formed, a buffer band-forming composition for imparting buffering properties to a bound shape, and various functional liquid materials. Supported adsorbing composition, heat-resistant fire-resistant composition, heat insulation or heat-insulating composition that exhibits heat-insulating properties or heat-retaining properties, precipitation-aggregating composition that promotes solid-liquid separation, or various functionalities 14. A powder or a granular material comprising a compound or composition for improving / improving the physical properties or functionality of a binder-shaped body to be modified, which is selected from the group of compositions alone or in combination of two or more kinds. Modification processing method. 前記の機能付与剤であるレインホースメントが、結着形状体を補強・補足する繊維質組成物、同様に細骨材ないしは粗骨材の群より選ばれる単独ないし2種以上の組み合わせの補強性材料である請求項13記載の改質処理方法。  Reinforcement as the above-mentioned function-imparting agent is a fibrous composition that reinforces and supplements the bound shape, as well as a single or a combination of two or more selected from the group of fine aggregates or coarse aggregates. The reforming method according to claim 13, which is a material. 前記の原位置非成型品が、原位置に持ち込んで施設された処理装置により、原位置に存在して有害物質を共存する汚染土壌地盤の乾燥物基準で100質量部に対して、改質処理剤を5ないし30質量部、汚必要に応じて機能付与剤を400質量部以下の量で加え、さらに染土壌地盤が保有している水分を勘案して水系溶媒を少なくとも20質量部以上になる量で混和して活性化混和物を原位置で調整され、次いで原位置で調製された活性化混和物に対して加工工程を経ることなく原位置における環境下の常温雰囲気中に少なくとも24時間曝露養生することにより土壌地盤、軟弱地盤、道路、堤ないしは農地・宅地・公共用地に無害化処理および形状化処理が施されている結着形状体である請求項12記載の改質処理方法。  The in-situ non-molded product is reformed with respect to 100 parts by mass on the basis of the dry matter of the contaminated soil ground that exists in-situ and coexists with harmful substances by the processing equipment brought in place 5 to 30 parts by weight of the agent, and if necessary, the function-imparting agent is added in an amount of 400 parts by weight or less, and the water-based solvent is at least 20 parts by weight in consideration of the water content of the dyed soil ground. The activated admixture is adjusted in-situ by mixing in quantities, and then exposed to the in-situ ambient ambient atmosphere for at least 24 hours without any processing steps on the in-situ prepared activated admixture. 13. The reforming method according to claim 12, wherein the reforming method is a binding shape body in which soil soil, soft ground, roads, dikes, or farmland / residential land / public land are subjected to detoxification treatment and shaping treatment by curing. 前記の形状加工成型品が、原位置に持ち込んで施設された処理装置により、原位置に存在して有害物質を共存する汚染土壌地盤、汚染軟弱地盤、汚染道路・堤ないしは汚染農地・宅地・公共用地の乾燥物基準で100質量部に対して、改質処理剤を5ないし30質量部、必要に応じて機能付与剤を400質量部以下の量で加え、さらに汚染土壌地盤が保有している水分を勘案して水系溶媒を少なくとも20質量部以上になる量で混和して活性化混和物を原位置で調整され、次いで原位置で調製された活性化混和物を塊状物、杭状物、農地畦、側溝、道路、堤ないしは構造物からなる形状化処理物に加工し、次いで原位置で混和・加工された形状化処理物を原位置における環境下の常温雰囲気中に少なくとも24時間曝露養生することにより塊状体、杭状体、農地畦、側溝、道路、堤ないし構造体に無害化処理および形状化処理が施されている結着形状体である請求項12記載の改質処理方法。  Contaminated soil ground, contaminated soft ground, contaminated road / bank or contaminated farmland / residential land / public where the above-mentioned shape-processed molded product is brought into place and installed at the facility and is present at the site and coexist with harmful substances 5 to 30 parts by mass of the modifying treatment agent is added to 100 parts by mass on the basis of the dry matter of the site, and the function-imparting agent is added in an amount of 400 parts by mass or less as necessary. In consideration of moisture, the aqueous solvent is mixed in an amount of at least 20 parts by mass or more, and the activated admixture is adjusted in situ, and then the activated admixture prepared in situ is a lump, pile, Processed into a shaped product consisting of farmland ridges, ditches, roads, levee or structures, and then exposed to at least 24 hours in the normal temperature atmosphere in the original environment. Lump by Body, pile-shaped body, farmland furrow, gutters, roads, modification processing method of claim 12, wherein a binder shaped body detoxification the banks to the structure and shaping treatment is applied. 前記の耐水性粉粒体品ないしは形状加工成型品が、持込位置に存在して有害物質を共存する熱履歴シリケートを乾燥物基準で100質量部に対して、改質処理剤を5ないし30質量部、必要に応じて機能付与剤を400質量部以下の量で加え、さらに熱履歴シリケートおよび改質処理剤が保有している水分を勘案して水系溶媒を少なくとも20質量部以上になる量で混和して活性化混和物を持込位置で調整され、次いで持込位置で調製された活性化混和物を粉粒物、砂粒物、顆粒物、造粒物、硬化・固化物、構造物、管状物、線状物、多孔質体ないしは形状化物からなる耐水性粉粒体物ないしは形状加工成型物である形状化処理物に加工し、次いで持込位置で混和・加工された形状化処理物を持込位置における環境下の常温雰囲気中に少なくとも24時間曝露養生することにより粉粒体、砂粒体、顆粒体、造粒体、硬化・固化体、構造体、柱状体、管状体、線状体、板状体、膜状体、多孔質体ないしは形状化体に無害化処理および形状化処理が施されている結着形状体である請求項12記載の改質処理方法。  The above-mentioned water-resistant granular product or shape-processed molded product is present in the carry-in position and the heat history silicate coexisting with harmful substances is 100 parts by mass on a dry matter basis, and 5 to 30 modifiers are added. Part by mass, if necessary, adding a function-imparting agent in an amount of 400 parts by mass or less, and further taking into account the water held by the heat history silicate and the modification treatment agent, so that the aqueous solvent is at least 20 parts by mass or more The activated admixture is adjusted at the carry-in position by mixing in, and then the activated admixture prepared at the carry-in position is granulated, sand granule, granule, granulated product, hardened / solidified product, structure, Shaped processed product processed into a shaped processed product that is a water-resistant granular material or shaped processed product consisting of a tubular product, a linear product, a porous material or a shaped product, and then mixed and processed at the carry-in position In a room temperature atmosphere under the environment Can be exposed to 24 hours of exposure and curing, granule, sand granule, granule, granulation, cured / solidified, structure, columnar, tubular, linear, plate, membrane, porous The modification treatment method according to claim 12, which is a binding shape body in which the body or the shaped body is subjected to a detoxification process and a shaping process. 請求項1ないしは11のいずれか1項記載の改質処理剤を活用する請求項12ないしは23のいずれか1項記載の改質処理方法における混和工程で調製される流動性活性化混和物を予め用意された応用対象基材に付着せしめる加工工程により付着化処理物として調製し、次いで該付着化処理物を所定雰囲気中に開放せしめて応用対象基材と一体化された結着形状体とする養生工程で構成される一連の作業工程からなる改質処理方法において;
上記の流動性活性化混和物が、原位置または持込位置に存在する熱履歴シリケートを乾燥物基準で100質量部に対して、改質処理剤を乾燥物基準で2ないし20質量部未満を加え、必要に応じて機能付与剤を400質量部以下の量で付加して混和して活性化混和物とし、該活性化混和物中の含有水分の含水率が35ないし70質量%範囲に確保される状態になるように水系溶媒を加えて量割合を調整して混和し、該活性化混和物が常温にて混和・放置される3時間の間のpH値が12を超える状態が確保されて可塑状、マヨネーズ状、糊状ないしはスラリー状に調製されている混和物であり;
上記の応用対象基材が、無機質材質、岩石・粘土材質、水和鉱物材質、セラミックス・窯業材質、金属材質、木材質、繊維材質、有機質材質ないしはこれら材質の複合材質からなる粉粒体、吸着性粉粒体、砂粒体、顆粒体、造粒体、硬化・固化体、構造体、床体、柱状体、管状体、線状体、板状体、膜状体、ガラクタ体ないしは形状化体であり;
上記の加工工程が、上記の流動性活性化混和物を応用対象基材の表面に所定量の割合で展延、固結、結着、付着、被覆、積層、集合または注入からなる加工手段により目的・用途に応じた応用対象基材と一体化された基材付着型の活性粉体結着物、基材積層複合物、顆粒群体集合物ないしは注充填一体化物からなる付着化処理物とする工程であり;
上記の養生工程が、該応用対象基材と一体化された付着化処理物を常温から100℃範囲にある常圧、加圧、減圧条件下における気中、水中、海中、土中、溶液中、蒸気中、非酸素ガス中の雰囲気の群より選ばれる単独雰囲気中ないし2種以上の組み合わせの多段雰囲気中に少なくとも15分間解放して反応・養生が進行して結着硬化の完了している基材付着型の活性粉体結着品、基材積層複合品、顆粒群体集合品ないしは注充填一体化品からなる応用対象基材と一体化された結着形状体とする工程であり;
上記の改質処理方法が、熱履歴シリケートを改質対象素材として、上記の一連の作業工程に付して調製される流動性活性化混和物のアルカリ性成分を固定化してpH10未満が確保され、該改質対象素材に有害物質が共存するときは該有害物質を固定・不溶化する無害化処理を施し、同時に粉粒体の熱履歴シリケートを耐水性で水中再泥化しない形状化処理を施して応用対象基材と一体化された基材付着型の結着形状体に改質処理することを特徴とする改質処理方法。
24. The fluid activated admixture prepared in the blending step in the reforming treatment method according to any one of claims 12 to 23, wherein the reforming treatment agent according to any one of claims 1 to 11 is utilized. It is prepared as an adhering treatment product by a processing step for adhering to the prepared application target substrate, and then the adhering treatment product is opened in a predetermined atmosphere to form a binding shape body integrated with the application target substrate. In a reforming method comprising a series of work steps composed of curing steps;
The fluidity activated admixture is 100 parts by mass of the heat history silicate present in the original position or the carry-in position on the basis of dry matter, and 2 to less than 20 parts by mass of the modification treatment agent on the basis of dry matter. In addition, if necessary, a function-imparting agent is added in an amount of 400 parts by mass or less and mixed to make an activated admixture, and the moisture content of the water content in the activated admixture is ensured in the range of 35 to 70% by mass. As a result, an aqueous solvent is added to adjust the volume ratio so as to be in a mixed state, and the activated mixture is mixed and allowed to stand at room temperature. An admixture prepared in the form of a plastic, mayonnaise, paste or slurry;
The above-mentioned application target base material is an inorganic material, rock / clay material, hydrated mineral material, ceramics / ceramic material, metal material, wood material, fiber material, organic material or a composite material of these materials, adsorption Powder, sand, granule, granulated, hardened / solidified, structure, floor, columnar, tubular, linear, plate, film, galactor or shaped Is;
The above processing step is performed by processing means comprising spreading, solidifying, binding, adhering, coating, laminating, assembling, or pouring the above fluid activated admixture on the surface of the substrate to be applied at a predetermined rate. A process for forming an adherent treated product comprising a base-attached active powder binder integrated with a base material to be applied according to the purpose and use, a base laminate composite, an aggregate of granules, or an injection-filled integrated body Is;
The above curing process is performed in the atmosphere, water, sea, soil, and solution under normal pressure, pressure, and reduced pressure conditions in the range from room temperature to 100 ° C. In a single atmosphere selected from the group of atmospheres in steam and non-oxygen gas or in a multistage atmosphere of a combination of two or more, the reaction / curing progresses for at least 15 minutes to complete the binding and curing. A process for forming a binder-shaped body integrated with a base material to be applied consisting of a base-attached active powder binder, a base-layer composite, a granule aggregate assembly or an injection-filled integrated product;
The above reforming treatment method uses a heat history silicate as a material to be reformed, immobilizes the alkaline component of the fluidity activated admixture prepared by the above-described series of work steps, and ensures a pH of less than 10. When harmful substances coexist in the material to be modified, a detoxification treatment is performed to fix and insolubilize the harmful substances, and at the same time, a heat history silicate of the granular material is water-resistant and shaped to prevent re-mudging in water. A reforming method characterized in that a reforming process is performed on a substrate-attached binding body integrated with an application target substrate.
前記の活性粉体結着品が、予め混和工程で調製された可塑状、マヨネーズ状、糊状ないしはスラリー状の流動性活性化混和物を粉粒体状の応用対象基材表面に所定量の割合で付着・被覆・結着して付着化処理物とする加工工程において、該応用対象基材が比表面積100m/g以上を有する吸着性粉粒体である炭類、非晶質シリカ、活性ケイ酸、活性ケイ酸塩、珪藻土、活性アルミナ、活性アルミノケイ酸塩化合物、含炭素乾留品、吸着性焼却灰ないしはゼオライトの群より選ばれる単独ないし2種以上の組み合わせ吸着性粉粒体基材であり、該吸着性粉粒体100質量部に対して、流動性活性化混和物の100ないしは400質量部を加えて混和しながら吸着性粉粒体基材の表面を濡らしつつ粉粒物、顆粒物ないしは形状化物である活性粉体結着物からなる付着化処理物に加工付着、被覆、結着せしめ、次いで該付着化処理物を養生工程に付する一連の作業工程により、有害化学物質を共存して粉粒体の該熱履歴シリケートが、吸着性が確保された不特定形状の粉粒体、顆粒体ないし形状化体からなる応用対象基材と固結一体化されている付着型の結着形状体である請求項24記載の改質処理方法。The above-mentioned active powder binder is prepared by applying a predetermined amount of a fluid, activated, admixture in the form of plastic, mayonnaise, paste, or slurry prepared in the mixing step to the surface of the substrate to be applied in the form of granules. In the processing step of attaching / coating / binding at a ratio to obtain an adhering treatment product, the application target substrate is an adsorbent granular material having a specific surface area of 100 m 2 / g or more, carbon, amorphous silica, Active silicic acid, activated silicate, diatomaceous earth, activated alumina, activated aluminosilicate compound, carbon-containing carbonized product, adsorptive incineration ash or zeolite, or a combination of two or more adsorbent powder base materials In addition, 100 to 400 parts by mass of the fluidized activated admixture is added to 100 parts by mass of the adsorbent granular material, and the granular material while wetting the surface of the adsorbent granular substrate while mixing, Active as a granule or shaped product By a series of work steps in which an adhesion treatment product composed of a powder binder is processed, adhered, coated, and bonded, and then the adhesion treatment product is subjected to a curing step, the harmful particles are coexisting with the chemical substance. The heat history silicate is an adhesion-type binder-shaped body that is solidified and integrated with a base material to be applied composed of an unspecified powder particle, granule, or shaped body with ensured adsorptivity. 24. The reforming method according to 24. 前記の基材積層複合品が、加工工程において、混和工程で調製された可塑状、マヨネーズ状、糊状ないしはスラリー状の流動性活性化混和物を予め用意された応用対象基材の表面上に所定量の割合で応用対象基材と一体化された付着化処理物とする工程において、該応用対象基材が、無機質材質、岩石・粘土材質、水和鉱物材質、セラミックス・窯業材質、金属材質、木材質、繊維材質、有機質材質ないしはこれら材質の複合材質からなる顆粒体、造粒体、硬化・固化体、構造体、床対、柱状体、管状体、線状体、板状体、膜状体、ガラクタ体ないしは形状化体からなる形状の確保された基材であり、該基材の表面に該流動性活性化混和物が展延、結着、付着、被覆または積層からなる加工手段により目的・用途に応じた応用対象基材と一体化された基材積層複合物らなる付着化処理物とし、次いで該付着化処理物を養生工程に付する一連の作業工程により、有害化学物質を共存して粉粒体の該熱履歴シリケートが、不特定形状の粉粒体、顆粒体ないし形状化体からなる応用対象基材と積層一体化されている付着型の結着形状体である請求項24記載の改質処理方法。  In the processing step, the above-mentioned substrate laminated composite product is formed on the surface of the base material to be applied in which the fluidized activated admixture of plastic, mayonnaise, paste or slurry prepared in the mixing step is prepared in advance. In the process of making the adhering treatment integrated with the base material to be applied at a predetermined ratio, the base material to be applied is an inorganic material, a rock / clay material, a hydrated mineral material, a ceramic / ceramic material, a metal material. , Wood, fiber material, organic material or composite material of these materials, granulated body, hardened / solidified body, structure, floor pair, columnar body, tubular body, linear body, plate body, membrane A processing means comprising a base material having a shape, a rugged body, or a shaped body and having the fluidized activated admixture spread, bound, adhered, coated or laminated on the surface of the base material Integrated with the base material to be applied according to the purpose and application The heat treatment silicate of the granular material coexisting with harmful chemical substances through a series of work steps in which the adherend treated product is subjected to a curing process, and the adhering treated product is made into a base material laminated composite. 25. The modification treatment method according to claim 24, wherein the modification treatment method is an adhesion-type binder-shaped body that is laminated and integrated with a base material to be applied that is formed of an unspecified shape of granular material, granule, or shaped body. 前記の顆粒群体集合品が、加工工程において、混和工程で調製された可塑状、マヨネーズ状、糊状ないしはスラリー状の流動性活性化混和物を予め用意された応用対象基材の表面上に所定量の割合で応用対象基材と一体化された付着化処理物とする工程において、該応用対象基材が、無機質材質、岩石・粘土材質、水和鉱物材質、セラミックス・窯業材質、金属材質、木材質、繊維材質、有機質材質ないしはこれら材質の複合材質からなる顆粒体、造粒体、ガラクタ体ないしは形状化体からなる形状の確保された顆粒状基材であり、該基材の表面に該流動性活性化混和物が混和、結着、付着、被覆または積層からなる加工手段により目的・用途に応じた顆粒状の応用対象基材と一体化された顆粒群体集合物からなる付着化処理物とし、次いで該付着化処理物を養生工程に付する一連の作業工程により、有害化学物質を共存して粉粒体の該熱履歴シリケートが、不特定形状の粉粒体、顆粒体ないし形状化体からなる応用対象基材と一体化されている付着型の結着形状体である請求項24記載の改質処理方法。  In the processing step, the aggregated product of the granules is placed on the surface of the base material to be applied in which a plastic, mayonnaise, paste or slurry fluid activated admixture prepared in the blending step is prepared in advance. In the process of making the adhering treatment product integrated with the base material to be applied at a fixed ratio, the base material to be applied is an inorganic material, a rock / clay material, a hydrated mineral material, a ceramic / ceramic material, a metal material, A granular material made of wood material, fiber material, organic material or a composite material of these materials, a granulated material, a granulated material made of a galactor material or a shaped material, and a granular material with a secured shape on the surface of the substrate. Adhesive treatment product composed of aggregates of granular aggregates integrated with a granular application target substrate according to the purpose and application by processing means in which the fluidity activated admixture is mixed, bound, adhered, coated or laminated. And then An application in which the heat history silicate of a granular material coexists with toxic chemical substances and consists of an unspecified shaped granular material, granule, or shaped body, through a series of work steps in which the treated material is subjected to a curing process. The reforming method according to claim 24, wherein the reforming method is an adhesion-type binding shape body integrated with a target substrate. 前記の注充填一体化品が、有害物質類もしくは低レベルの放射性物質を共存している顆粒状またはガラクタ状類の塊状物からなる顆粒群集合体、また既存の無機質である顆粒状ないしガラクタ状の塊状物からなる小塊群集合体を容器に収納した容器収納ガラクタ集合群体からなる応用対象基材と一体化された付着化処理物とする工程において、該容器収納ガラクタ集合群体の収めてある容器中に流動性活性化混和物を容器中全体に注入充填してガラクタ集合群体からなる応用対象基材と一体化された注充填一体化物からなる付着化処理物とし、次いで該付着化処理物を養生工程に付する一連の作業工程により、有害化学物質を共存して粉粒体の該熱履歴シリケートが、不特定形状の粉粒体、顆粒体ないし形状化体からなる応用対象基材と一体化されている付着型の結着形状体である請求項24記載の改質処理方法。  The above-mentioned injection-filled integrated product is a granular group aggregate composed of granular or galactic aggregates coexisting with harmful substances or low-level radioactive substances, or existing granular or galactic granular materials. In the step of forming an adhering treatment integrated with a base material to be applied consisting of a container-accommodating garment aggregate group in which a small blob group aggregate consisting of lumps is contained in a container, in the container in which the container-accommodating gargle aggregate group is stored The fluidized activated admixture is injected and filled into the entire container to form an adhesion-treated product consisting of a pouring-filled integrated material integrated with a base material to be applied consisting of a garacter aggregate, and then curing the adhesion-treated product. Through a series of work steps attached to the process, the heat history silicate of the granular material coexisting with harmful chemical substances is integrated with the application target base material consisting of unspecified shaped granular material, granule or shaped body Modification processing method of claim 24 wherein the adhesion-type binder shape of being. 請求項1ないし11のいずれか1項記載の改質処理剤を活用して、休眠成分からなる熱履歴シリケートを改質対象素材とし、少なくとも常温における請求項12ないし28のいずれか1項記載の改質処理方法に付して、pH12が確保されている活性化混和物を調製し、さらに必要に応じて形状化処理物ないしは付着化処理物を調製し、次いで活性化混和物、ないしは形状化処理物または付着化処理物におけるアルカリ性成分を固定化してpH10未満が確保され、該改質対象素材に有害物質が共存するときは該有害物質を中性域ならびに酸性域における溶出試験で環境基準値以下の範囲に固定・不溶化する無害化処理が施され、同時に粉粒体の熱履歴シリケートを耐水性で水中再泥化しない形状化処理が施されている自己完結型の原位置非成型品、耐水性粉粒体品、形状加工成型品、さらに基材付着型の活性粉体結着品、基材積層複合品、顆粒群体集合品または注充填一体化品であることを特徴とする結着形状体。  The modification treatment agent according to any one of claims 1 to 11 is used, and a heat history silicate composed of a dormant component is used as a material to be modified, and at least at normal temperature, the composition according to any one of claims 12 to 28. By applying the modification treatment method, an activated admixture having a pH of 12 is prepared, and if necessary, a shaped treated product or an attached treated product is prepared, and then the activated blended product or shaped product is prepared. When the alkaline component in the treated product or the adherend-treated product is fixed to ensure a pH of less than 10 and harmful substances coexist in the material to be modified, the environmental standard value is determined in the elution test in the neutral and acidic ranges. Self-contained in-situ non-destructive treatment that is fixed and insolubilized in the following range, and at the same time is shaped so that the heat history silicate of the granule is water resistant and does not re-mudder in water It is a molded product, a water-resistant granular product, a shape-processed molded product, a base material-attached active powder binder product, a base material laminated composite product, a granule aggregate assembly product, or an injection-filled integrated product. Binding shape body. 前記の原位置非成型品が、原位置に存在して有害元素群ないしダイオキシン類を環境基準値以上の量で共存して汚染している土壌地盤、軟弱地盤、道路・堤・法面ないしは農地・宅地・工業用地・公共用地を改質対象素材とし、少なくとも常温において改質処理剤を活用する一連の作業工程からなる改質処理方法に付して、有害元素群ないしダイオキシン類を共存して粉粒体の該熱履歴シリケートが、外圧に変動性を示す状態に結着・硬化して水中再泥化しない耐水性の有用土壌地盤、軟弱地盤、道路・堤・法面ないしは農地・宅地・公共用地に無害化処理ならびに形状化処理が施されている請求項29記載の結着形状体。  Soil ground, soft ground, roads / banks / slopes or farmland where the above-mentioned non-molded product is in situ and contaminates with harmful elements or dioxins in an amount exceeding the environmental standard value.・ Use residential land / industrial land / public land as a material to be reformed, and attach it to a reforming process consisting of a series of work processes that utilize a reforming agent at least at room temperature, and coexist with harmful elements or dioxins. The heat history silicate of the granular material binds and hardens in a state showing variability in external pressure, and does not re-mudging in water.Water-resistant useful soil ground, soft ground, roads, dikes, slopes, or farmland, residential land, 30. The binding shape body according to claim 29, wherein the public land is subjected to a detoxification process and a shaping process. 前記の形状加工成型品が、原位置に存在して有害元素群ないしダイオキシン類を環境基準値以上の量で共存して汚染されている土質土壌、建築・土木関連廃土、窯業関連廃物、ケイ酸塩系投棄廃棄物類、汚泥・底質・脱水ケーキ類、焼却灰類を改質対象素材とし、原位置で少なくとも常温において改質処理剤を活用する一連の作業工程からなる改質処理方法に付して、有害元素群ないしはダイオキシン類を共存して粉粒体の該熱履歴シリケートが、一軸圧縮強度で500KN/m以上の強度が確保される状態に結着・硬化して水中再泥化しない耐水性の塊状体、杭状体、農地畦、側溝、道路、堤ないし構造体に無害化処理ならびに形状化処理が施されている請求項29記載の結着形状体。The above-mentioned shape-processed molded products are in situ, contaminated with soils that are contaminated by coexisting harmful elements or dioxins in an amount exceeding the environmental standard value, architectural / civil engineering related waste, ceramic industry related waste, A reforming treatment method consisting of a series of work processes that use acid-based dumping waste, sludge, sediment, dewatered cakes, incinerated ash, etc., and the reforming agent at the normal temperature at least at the normal temperature. In addition, the heat history silicate of the granular material coexisting with a harmful element group or dioxins is bound and cured in a state where a uniaxial compressive strength of 500 KN / m 2 or more is ensured, and the 30. The bound shaped body according to claim 29, wherein the water-resistant mass, pile-shaped body, agricultural landfill, gutter, road, bank, or structure that is not mudified is subjected to a detoxification process and a shaping process. 前記の形状加工成型品が、原位置または持込位置に存在して有害化学物質を共存する熱履歴シリケートを改質対象素材とし、少なくとも常温において改質処理剤を活用する一連の作業工程からなる改質処理方法に付して、有害化学物質を共存して粉粒体の該熱履歴シリケートが、一軸圧縮強度で500KN/m以上の強度が確保される状態に結着・硬化して水中再泥化しない耐水性の粉粒体、砂粒体、顆粒体、造粒体、硬化・固化体、構造体、柱状体、管状体、線状体、板状体、膜状体、多孔質体ないしは形状化体に無害化処理ならびに形状化処理が施されている請求項29記載の結着形状体。The shape-processed molded product consists of a series of work steps that use a heat treatment silicate that is present in the original position or in the carry-in position and coexists with harmful chemical substances as a material to be modified, and that utilizes a modification treatment agent at least at room temperature. When subjected to the modification treatment method, the heat history silicate of the granular material coexisting with harmful chemical substances is bound and hardened in a state in which a uniaxial compressive strength of 500 KN / m 2 or more is ensured, and the Water-resistant granule, sand granule, granule, granulated body, cured / solidified body, structure, columnar body, tubular body, linear body, plate-like body, film-like body, porous body without re-mudging 30. The bound shaped body according to claim 29, wherein the shaped body is subjected to a detoxification process and a shaping process. 前記の耐水性粉粒体品が、原位置または持込位置に存在して有害化学物質を共存する熱履歴シリケートを改質対象素材とし、少なくとも常温において改質処理剤を活用する一連の作業工程からなる改質処理方法に付して、有害化学物質を共存して粉粒体の該熱履歴シリケートが、砂粒状ないし顆粒状の再生砂、再生土、再生骨材、流動化処理材、覆砂材、中込材、造成材、盛土材、築堤材、土壌改良材、客土材の群からなる土木用資材、また植栽用土、造園用資材、緑化基盤材、目土の群からなる植物育成資材からなる無害化処理ならびに形状化処理が施されている請求項29記載の結着形状体。  A series of work steps in which the above water-resistant granular product is a material to be reformed, which is present in the original position or in the carry-in position and coexists with harmful chemical substances, and the reforming agent is utilized at least at room temperature. The heat history silicate in the form of granular material in the presence of a harmful chemical substance is subjected to sand-like or granulated reclaimed sand, reclaimed soil, reclaimed aggregate, fluidized treatment material, covering Civil engineering materials consisting of sand, medium-filled materials, reclaimed materials, embankment materials, embankment materials, soil improvement materials, guest soil materials, planting soil, landscaping materials, greening base materials, plants consisting of soil groups 30. The binding shape body according to claim 29, wherein a detoxification process and a shaping process comprising a growing material are performed. 前記の形状加工成型品が、持込位置に存在する熱履歴シリケート、ないしは有害物質を共存する熱履歴シリケートを改質対象素材とし、予め混和工程において糊状ないし可塑状に調製されている流動性活性化混和物を調製し、該流動性混和物をプラスチック製の基材・型類表面に1ないしは20mm厚の膜状、板状、塗膜状もしくはフィルム状の膜状物とし、養生工程において養生条件下で養生した後、基材・型類より脱着せしめる一連の作業工程からなる改質処理方法に付することにより、有害化学物質を共存して粉粒体の該熱履歴シリケートが、不定形ないし定形の膜状、板状、フイルム状の膜状資材からなる無害化処理ならびに形状化処理が施されている請求項29記載の結着形状体。  The above-mentioned shape-processed molded product has a heat history silicate present in the carry-in position or a heat history silicate coexisting with harmful substances as a material to be modified, and is fluidized in advance in a paste or plastic form in the mixing step An activated admixture is prepared, and the fluid admixture is formed into a film-like, plate-like, film-like or film-like film-like material having a thickness of 1 to 20 mm on the surface of a plastic substrate or mold, and in the curing process. After curing under curing conditions, it is subjected to a reforming method consisting of a series of work steps that are desorbed from the substrate and molds, so that the thermal history silicate of the granular material is not coexisting with harmful chemical substances. 30. The binding shape body according to claim 29, wherein a detoxification treatment and a shaping treatment comprising a film-form material of a regular form or a regular form, a plate form, or a film form are performed. 前記の形状加工成型品が、持込位置に存在して有害物質を共存して、含水比が150より大きい含水ヘドロ・底質類または農業集落排水・上水・下水の汚泥類であるときは予め含水比150未満に脱水処理もしくは既に含水比150未満である含水汚泥類を改質対象素材とし、少なくとも常温において改質処理剤を活用する一連の作業工程からなる改質処理方法に付することにより、有害化学物質を共存して粉粒体の該熱履歴シリケートが、一軸圧縮強度で500KN/m以上の強度が確保される状態に結着・硬化して水中再泥化しない耐水性の粉粒体、砂粒体、顆粒体、硬化体、構造体、固化体、成型体、膜状体、形状体、フイルム・膜状体、機能性保有被覆体、積層・塗布体、顆粒群集合体ないしは注充填一体化体に無害化処理ならびに形状化処理が施されている請求項29記載の結着形状体。When the shape-processed molded product is a water-containing sludge, bottom sediment, or agricultural settlement drainage, clean water, sewage sludge that is present in the carry-in position and coexists with harmful substances and has a water content ratio of more than 150 A dehydration treatment with a water content ratio of less than 150 in advance or a water treatment sludge having a water content ratio of less than 150 as a material to be reformed and subjected to a reforming treatment method comprising a series of work steps utilizing a reforming agent at least at room temperature. Therefore, the heat history silicate of the granular material coexisting with harmful chemical substances is water-resistant so that it does not re-mudder in water by binding and hardening to a state where a uniaxial compressive strength of 500 KN / m 2 or more is secured. Powder, sand granule, granule, hardened body, structure, solidified body, molded body, film-like body, shape body, film / film-like body, functional possession covering body, laminated / coated body, granule group aggregate or Detoxification treatment and integrated packing 30. The bound shape body according to claim 29, wherein a shape treatment is applied to the body. 前記の含水の底質もしくは農業集落排水・上水・下水の汚泥が、水に分散している含水土質・汚泥・アオコ・藻類群からなる浮遊物に対して、ファンクショメントである沈降凝集組成物を水中に撒布して加え撹拌して、水分散性の浮遊物を水中で予め凝集沈降せしめ、水中底部底質として回収される含水泥土類からなる改質対象素材とし、少なくとも常温において改質処理剤を活用する一連の作業工程からなる改質処理方法に付に付して、該熱履歴シリケートに無害化処理ならびに形状化処理が施されている形状加工成型品である請求項35記載の結着形状体。  Sedimentation and agglomeration composition that is a function of suspended matter composed of hydrous soil, sludge, blue-green, algae group in which the above-mentioned water-containing bottom sediment or agricultural settlement drainage, clean water, sewage sludge is dispersed in water Disperse the material in water and stir to coagulate and settle the water-dispersible suspended solids in water in advance, making it a material to be reformed consisting of hydrous mud collected as bottom sediment in water, and reforming at least at room temperature 36. A shape-processed molded product in which the heat history silicate is subjected to a detoxification process and a shaping process in addition to a modification treatment method comprising a series of work steps utilizing a treatment agent. Binding shape body. 含リン焼却灰
前記の耐水性粉粒体品ないしは形状加工成型品が、持込位置に存在して有害元素群を環境基準値以上の量で共存して汚染されており、リン成分を含有する下水や農業集落排水の含水汚泥の焼却灰を水分調整剤として下水や農業集落の含水汚泥に加えて混合され、さらに必要に応じてファンクショメントの機能付与組成物である消臭剤類を加えて調整混合されている下水・農業集落排水の焼却灰が複合している熱履歴シリケートであり、該有害物質共存の改質対象素材に改質処理剤を活用する一連の作業工程からなる改質処理方法に付することにより、有害化学物質を共存して粉粒体の該熱履歴シリケートが、植物育成材、緑化基盤材、目土材、客土材、埋戻材、土質作業性改良材ないしは土壌改良材に無害化処理および形状化処理が施されている請求項29記載の結着形状体。
Phosphorus-containing incinerated ash The above water-resistant granular product or shape-processed molded product is present in the carry-in position and is contaminated by the presence of harmful elements in an amount exceeding the environmental standard value, and contains a phosphorus component Incinerated ash from the sewage and agricultural village drainage sludge is mixed with the sewage and agricultural village sewage sludge as a moisture regulator, and if necessary, deodorizers that are function-enhancing compositions are added. This is a heat history silicate compounded with incinerated ash from sewage and agricultural settlement wastewater that has been adjusted and mixed, and consists of a series of work processes that utilize a modification treatment agent as a material to be reformed in the presence of the hazardous substances. By applying to the treatment method, the thermal history silicate of the granular material coexisting with harmful chemical substances, plant growth material, greening base material, joint soil material, customer soil material, backfill material, soil workability improvement material Or detoxification treatment and shaping treatment for soil amendment 30. The bound shape body according to claim 29, wherein the treatment is performed.
機能付与剤が活性化成分に補足されている処理材
前記の形状加工成型品が、持込位置に存在して有害物質を共存する熱履歴シリケートを改質対象素材とし、改質処理剤100質量部に対して、機能付与剤であるファンクショメントである耐熱火組成物ないし断熱・保温組成物を100質量部以上の量で付加補足されている機能付加成分を活用する一連の作業工程からなる改質処理方法に付することにより、有害化学物質を共存している粉粒体の該熱履歴シリケートが、不焼成または焼成された特定または不特定の耐熱・保温築炉材、セラミックス品、レンガ・耐火材・断熱材ないしは保温・断熱材とする無害化処理および形状化処理が施されている請求項29記載の結着形状体。
A processing material in which a function-imparting agent is supplemented by an activation component The above-mentioned shape-processed molded product is a heat history silicate that is present at the carry-in position and coexists with harmful substances, and the modifying target material is 100 mass. It consists of a series of work steps that utilize function-added components supplemented with an amount of 100 parts by mass or more of a heat-resistant fire composition or a heat insulation / heat insulation composition that is a function that is a function-imparting agent. By applying the modification treatment method, the heat history silicate of the granular material coexisting with the harmful chemical substance is non-fired or fired specific or non-specific heat- and heat-retaining building materials, ceramic products, bricks 30. The binding shape body according to claim 29, wherein a detoxification treatment and a shaping treatment are performed as a refractory material, a heat insulating material, or a heat insulating and heat insulating material.
前記の形状加工成型品が、持込位置に存在して有害物質を共存する熱履歴シリケートを改質対象素材とし、改質処理剤100質量部に対して、機能付与剤であるファンクショメントの断熱・保温組成物、または10m/g以上の比表面積を有し0.05ないし1.2g/ccの範囲にあるかさ密度を有し、耐熱性の繊維状ないし粉粒体状のシリケートまたはケイ酸塩組成物からなるケイ酸カルシウム系化合物ないし保温・断熱材の廃材を100質量部以上の量で添加補足の改質処理剤を活用する一連の作業工程からなる改質処理方法に付することにより、有害化学物質を共存して粉粒体の熱履歴シリケートが、不焼成または焼成された特定または不特定の保温・断熱材、セラミックス品、レンガ・耐火材・断熱材とする無害化処理および形状化処理が施されている請求項29記載の結着形状体。The shape-processed molded product is a material that is a function-imparting agent with respect to 100 parts by mass of the modification treatment agent, with the heat history silicate that exists in the carry-in position and coexists with harmful substances as the material to be modified. A heat-insulating / heat-retaining composition, or a heat-resistant fibrous or granular silicate having a specific surface area of 10 m 2 / g or more and a bulk density in the range of 0.05 to 1.2 g / cc, or Calcium silicate compound consisting of a silicate composition or waste material of heat insulation / heat insulation material is added to a reforming method comprising a series of work steps utilizing an additional supplementary modifying agent in an amount of 100 parts by mass or more. By doing this, the heat history silicate of the granular material coexisting with harmful chemical substances is treated as non-fired or fired specific or non-specific heat insulation / insulation, ceramic products, bricks, refractories, and insulation. and Binder shaped body of claim 29, wherein Joka treated. 活性粉体結着品
前記の活性粉体結着品が、予め調製された可塑状、マヨネーズ状、糊状ないしスラリー状の流動性活性化混和物を粉粒体応用対象基材表面上に所定量の割合で応用対象基材と固結一体化された付着化処理物とする加工工程において、該応用対象基材が比表面積100m/g以上を有する吸着性粉粒体である炭類、非晶質シリカ、活性ケイ酸、活性ケイ酸塩、珪藻土、活性アルミナ、アルミノケイ酸塩化合物、含炭素乾留品、吸着性焼却灰ないしはゼオライトの群より選ばれる単独ないし2種以上の組み合わせ吸着性粉粒体基材に流動性活性化混和物を加えて混和して粉粒体応用対象基材表面を濡らしつつ粉粒物、顆粒物ないし形状化物である付着化処理物を経て付着、被覆、結着せしめる一連の作業工程により、粉粒体応用対象基材の吸着性が確保されて固結一体化された不特定形状の粉粒体、顆粒体ないし形状化体からなる請求項29記載の結着形状体。
Active powder-bound product The above-mentioned active powder-bound product is prepared by placing a pre-prepared plastic, mayonnaise, pasty or slurry-like fluid activated admixture on the surface of the base material to which the powder is applied. In the processing step to make the adhering treatment product consolidated and integrated with the application target base material at a fixed ratio, the application target base material is an adsorbent granular material having a specific surface area of 100 m 2 / g or more, Single or a combination of two or more adsorbent powders selected from the group of amorphous silica, activated silicic acid, activated silicate, diatomaceous earth, activated alumina, aluminosilicate compound, carbon-containing carbonized product, adsorptive incineration ash or zeolite Adhesion, coating, and binding through a granular, granule, or shaped adhering treatment product while wetting the surface of the base material to which the granular material is applied by adding a fluid activated admixture to the granular substrate By a series of working processes, Granular material of unspecified shape adsorptive target substrate is that with the consolidation integrated securing binder shaped body of claim 29 consisting of granules or shaped bodies.
基材積層複合品
前記の基材積層複合品が、持込位置に存在する熱履歴シリケート、ないしは有害物質を共存する熱履歴シリケートを改質対象素材とし、予め前記混和工程において糊状ないしは可塑状に調製されている流動性活性化混和物からなる糊状結着剤を調製し、該流動性混和物を予め用意された無機質資材、岩石・粘土類、窯業資材、木、繊維質、有機質、金属ないしは素材の複合素材により形成されている成型体、造成体ないしは型類体からなる基材類表面に塗装、接着、結着、被覆、多層塗り、どぶ浸け、まぶし、貼り付け、塗りつけ、吹き付け、流し込み、注入手段により塗布・被覆・結着せしめて積層加工層を形成複合せしめ、塗布物、被覆物、付着物、結着物、床状物または積層物からなる基材積層複合物とする一連の作業工程からなる改質方法に付することにより、有害化学物質を共存して粉粒体の該熱履歴シリケートが、剪断破壊付着力において200KN/m以上の付着力で確保された塗布体、被覆体、付着体、結着体、床状態もしくは積層体とする無害化処理および形状化処理が施されている請求項29記載の結着形状体。
Base laminate composite product The base laminate composite product is a heat history silicate present in the carry-in position or a heat history silicate coexisting with harmful substances as a material to be modified, and in the pasting step, a paste or plastic A paste-like binder composed of a fluidity activated admixture prepared in the above is prepared, and the fluidity admixture is prepared in advance with inorganic materials, rocks / clays, ceramic materials, wood, fibers, organic matter, Coating, bonding, binding, covering, multi-layer coating, soaking, spraying, pasting, smearing, spraying on the surface of a base material composed of a metal or composite material, or a body or mold A series of coating, coating, and binding by pouring, pouring, and forming a laminated processed layer to form a base composite composite consisting of a coating, coating, deposit, binding, floor, or laminate Work By applying the reforming method comprising the steps, the thermal history silicate of the granular material coexisting with harmful chemical substances, and the coated body and the coating in which the shear fracture adhesive force is secured with an adhesive force of 200 KN / m 2 or more 30. The binding shape body according to claim 29, wherein the body, the adhering body, the binding body, the floor state or the laminated body is subjected to a detoxification process and a shaping process.
前記の基材積層複合品において、予め調製された前記流動性混和物からなる糊状結着剤が、水系溶媒を介して、前記組成式(1)または(2)で表されるケイ酸アルカリの粉粒体ないし水混和体である活性化成分を改質して調製して、持込位置に存在して有害物質を共存する粉状体を改質対象素材として、一連の作業工程からなる改質方法に付することにより、pH4の酸性溶液に浸漬したとき固化体強度保持率が少なくとも80%確保されている塗布体、被覆体、付着体、結着体、成型体、床状体もしく積層体とする無害化処理ならびに形状化処理が施されている耐酸性の基材積層複合品である請求項41記載の結着形状体。  In the base laminate composite, the paste-like binder comprising the fluid mixture prepared in advance is an alkali silicate represented by the composition formula (1) or (2) via an aqueous solvent. It consists of a series of work steps, using a powdery substance that is prepared by modifying the active ingredient, which is a powder or water admixture, and that is a powdery substance that exists in the carry-in position and coexists with harmful substances. By applying the modification method, an applied body, a covering body, an adherent body, a bound body, a molded body, and a floor-shaped body having a solidified body strength retention rate of at least 80% when immersed in an acidic solution having a pH of 4 are also obtained. 42. The bound shape body according to claim 41, which is an acid-resistant base material laminated composite product that has been subjected to a detoxification treatment and a shape shaping treatment. 前記の顆粒群体集合品が、前記の顆粒体または骨材からなる顆粒群集合体、または既存の無機質で粒径が2ないし12mmφでかさ密度が0.2ないし3.5g/ccの球状、中空状、円柱状、フレーク状、顆粒状、不特定粒状、骨材状、不特定粒状、ガラクタ状もしくは粉粒状の集合群体を骨格素材として選び、持込位置に存在して有害物質を共存する改質対象素材を活用して予め流動性混和物を調製し、該骨格素材で構成される集合群体の表面全体を濡らせる量で該流動性混和物を加え、群体粒子の表面全体を結着剤で被覆・結着して集合群体を集合群体形状物とする一連の作業工程からなる改質方法に付することにより、顆粒体等の集合群体が一体化した粟オコシ状集合群体形状体として無害化処理ならびに形状化処理が施されている請求項29項記載の結着形状体。  The granule aggregate aggregate is a granule aggregate consisting of the granule or aggregate, or a spherical, hollow shape having a particle size of 2 to 12 mmφ and a bulk density of 0.2 to 3.5 g / cc. Columns, flakes, granules, unspecified granules, aggregates, unspecified granules, junk or powdery aggregates are selected as the skeletal material, and the modification target is present at the carry-in position and coexists with harmful substances Prepare a fluid admixture in advance using the material, add the fluid admixture in an amount that wets the entire surface of the aggregate composed of the skeletal material, and coat the entire surface of the cluster particles with a binder. -Detoxification treatment as a cocoon-like aggregated-group shaped body that aggregates aggregated bodies such as granules by subjecting it to a reforming method consisting of a series of work steps that bind and form an aggregated-group aggregate As well as shaping. Binder shape of Motomeko 29 Claims. 前記の顆粒体または骨材からなる顆粒群集合体、また既存の無機質である顆粒状ないしガラクタ状の有害物質類を共存する廃棄物類もしくは低レベルの放射性物質を共存している集合群体を容器に収納した容器収納ガラクタ集合群体に対して、水系溶媒による分散性混和物であり、必要に応じてインプルーブメントであるバリウム塩組成物の配合されたスラリー状混和物を注入充填による一連の作業工程からなる改質方法に付することにより、低レベルの放射性物質ないしは普通物質の集合群体が容器の中に封じ込められて一体化された状態に無害化処理ならびに形状化処理が施されている注充填一体化品である請求項29記載の結着形状体。  The above-mentioned granule group aggregate composed of granules or aggregates, as well as the aggregates coexisting with waste or low-level radioactive substances coexisting with existing inorganic granular or garlic harmful substances From a series of work steps by injection filling a slurry-like mixture containing a barium salt composition, which is a dispersible admixture with an aqueous solvent and, if necessary, an improvement, with respect to the container-contained trash assembly group By applying the reforming method, a low-level radioactive substance or a collection of ordinary substances is contained in a container and integrated into a state in which the detoxification process and the shaping process are performed. The bound shape body according to claim 29, which is a chemical product.
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Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2009001720A1 (en) * 2007-06-25 2008-12-31 Azmec Co., Ltd. Encapsulating agent for harmful substances and method for encapsulation of harmful substances
CN102078800A (en) * 2010-12-09 2011-06-01 苏州科技学院 Modified mineralized rubbish and preparation method thereof
KR101300740B1 (en) * 2011-12-08 2013-08-28 주식회사 포스코 Stabilizing method of ferro manganese dephosphorous slag
KR20150058873A (en) * 2013-11-21 2015-05-29 주식회사 포스코 Stabilizing method of slag
KR101717693B1 (en) * 2016-03-04 2017-03-24 주식회사 아이케이 Waterproof-structure for waste landfill and construction method thereof
CN109174044A (en) * 2018-08-30 2019-01-11 武汉理工大学 A method of improving opoka specific surface area and adsorption capacity
CN111847518A (en) * 2020-06-28 2020-10-30 广西锰华新能源科技发展有限公司 Efficient recycling method of silicomanganese slag
CN113368813A (en) * 2021-07-28 2021-09-10 山东亮剑环保新材料有限公司 Method for preparing honeycomb molecular sieve adsorbent by using red mud
CN114685068A (en) * 2022-02-08 2022-07-01 浙江红狮环保股份有限公司 Resource recycling method for high-content organic pharmaceutical chemical waste salt
EP4001237A4 (en) * 2019-06-20 2023-08-23 Fukko Co., Ltd. Blast furnace slag-type paint

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH11263661A (en) * 1998-01-13 1999-09-28 Nato Kenkyusho:Kk Hydraulic silica-based binder, and water and heat resistant solidified body
JP2002128550A (en) * 2000-10-16 2002-05-09 Natoo Kenkyusho:Kk Alkali-based curing agent and water resistant and heat resistant solidified body and its use
JP2002249348A (en) * 2001-02-16 2002-09-06 Natoo Kenkyusho:Kk Ordinary temperature hydraulic solidifying agent and water-and-heat-resistant porous solidified body
JP2004050158A (en) * 2002-07-17 2004-02-19 Natoo Kenkyusho:Kk Heavy metal immobilizing material and method for treating contaminated soil

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH11263661A (en) * 1998-01-13 1999-09-28 Nato Kenkyusho:Kk Hydraulic silica-based binder, and water and heat resistant solidified body
JP2002128550A (en) * 2000-10-16 2002-05-09 Natoo Kenkyusho:Kk Alkali-based curing agent and water resistant and heat resistant solidified body and its use
JP2002249348A (en) * 2001-02-16 2002-09-06 Natoo Kenkyusho:Kk Ordinary temperature hydraulic solidifying agent and water-and-heat-resistant porous solidified body
JP2004050158A (en) * 2002-07-17 2004-02-19 Natoo Kenkyusho:Kk Heavy metal immobilizing material and method for treating contaminated soil

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2009001720A1 (en) * 2007-06-25 2008-12-31 Azmec Co., Ltd. Encapsulating agent for harmful substances and method for encapsulation of harmful substances
JP5697334B2 (en) * 2007-06-25 2015-04-08 学校法人早稲田大学 Heavy metal insolubilizer and method for insolubilizing heavy metal
CN102078800A (en) * 2010-12-09 2011-06-01 苏州科技学院 Modified mineralized rubbish and preparation method thereof
KR101300740B1 (en) * 2011-12-08 2013-08-28 주식회사 포스코 Stabilizing method of ferro manganese dephosphorous slag
KR20150058873A (en) * 2013-11-21 2015-05-29 주식회사 포스코 Stabilizing method of slag
KR101597713B1 (en) * 2013-11-21 2016-02-25 주식회사 포스코 Stabilizing method of slag
KR101717693B1 (en) * 2016-03-04 2017-03-24 주식회사 아이케이 Waterproof-structure for waste landfill and construction method thereof
CN109174044A (en) * 2018-08-30 2019-01-11 武汉理工大学 A method of improving opoka specific surface area and adsorption capacity
CN109174044B (en) * 2018-08-30 2021-02-19 武汉理工大学 Method for improving specific surface area and adsorption capacity of opal
EP4001237A4 (en) * 2019-06-20 2023-08-23 Fukko Co., Ltd. Blast furnace slag-type paint
CN111847518A (en) * 2020-06-28 2020-10-30 广西锰华新能源科技发展有限公司 Efficient recycling method of silicomanganese slag
CN113368813A (en) * 2021-07-28 2021-09-10 山东亮剑环保新材料有限公司 Method for preparing honeycomb molecular sieve adsorbent by using red mud
CN114685068A (en) * 2022-02-08 2022-07-01 浙江红狮环保股份有限公司 Resource recycling method for high-content organic pharmaceutical chemical waste salt

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