JPH07136693A - Sludge solidification agent - Google Patents
Sludge solidification agentInfo
- Publication number
- JPH07136693A JPH07136693A JP31596793A JP31596793A JPH07136693A JP H07136693 A JPH07136693 A JP H07136693A JP 31596793 A JP31596793 A JP 31596793A JP 31596793 A JP31596793 A JP 31596793A JP H07136693 A JPH07136693 A JP H07136693A
- Authority
- JP
- Japan
- Prior art keywords
- weight
- pts
- parts
- cement
- compound
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 239000003795 chemical substances by application Substances 0.000 title claims abstract description 35
- 239000010802 sludge Substances 0.000 title claims abstract description 22
- 238000007711 solidification Methods 0.000 title abstract description 18
- 230000008023 solidification Effects 0.000 title abstract description 18
- 239000004568 cement Substances 0.000 claims abstract description 26
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 14
- 239000002956 ash Substances 0.000 claims abstract description 14
- 150000001875 compounds Chemical class 0.000 claims abstract description 14
- 239000010881 fly ash Substances 0.000 claims abstract description 11
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 claims abstract description 9
- 229910021487 silica fume Inorganic materials 0.000 claims abstract description 9
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims abstract description 7
- 239000000377 silicon dioxide Substances 0.000 claims abstract description 7
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 claims abstract description 7
- 229910000288 alkali metal carbonate Inorganic materials 0.000 claims abstract description 6
- 150000008041 alkali metal carbonates Chemical class 0.000 claims abstract description 6
- 159000000007 calcium salts Chemical class 0.000 claims abstract description 5
- 239000000203 mixture Substances 0.000 claims description 8
- 101000617550 Dictyostelium discoideum Presenilin-A Proteins 0.000 claims 1
- 238000006243 chemical reaction Methods 0.000 abstract description 19
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 15
- 239000000126 substance Substances 0.000 abstract description 7
- 230000006872 improvement Effects 0.000 abstract description 5
- 239000002440 industrial waste Substances 0.000 abstract description 3
- 239000002689 soil Substances 0.000 description 23
- 238000012360 testing method Methods 0.000 description 23
- 239000005416 organic matter Substances 0.000 description 7
- JLDKGEDPBONMDR-UHFFFAOYSA-N calcium;dioxido(oxo)silane;hydrate Chemical compound O.[Ca+2].[O-][Si]([O-])=O JLDKGEDPBONMDR-UHFFFAOYSA-N 0.000 description 6
- 238000010276 construction Methods 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- 229910001653 ettringite Inorganic materials 0.000 description 5
- 239000003513 alkali Substances 0.000 description 4
- 239000007795 chemical reaction product Substances 0.000 description 4
- 238000012669 compression test Methods 0.000 description 4
- 238000005259 measurement Methods 0.000 description 4
- 235000019645 odor Nutrition 0.000 description 4
- 238000009933 burial Methods 0.000 description 3
- 238000005755 formation reaction Methods 0.000 description 3
- 238000009472 formulation Methods 0.000 description 3
- 230000005484 gravity Effects 0.000 description 3
- 229910001385 heavy metal Inorganic materials 0.000 description 3
- 238000006703 hydration reaction Methods 0.000 description 3
- 150000002500 ions Chemical class 0.000 description 3
- 239000000047 product Substances 0.000 description 3
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 2
- 230000009471 action Effects 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 229940043430 calcium compound Drugs 0.000 description 2
- 150000001674 calcium compounds Chemical class 0.000 description 2
- 239000000378 calcium silicate Substances 0.000 description 2
- 229910052918 calcium silicate Inorganic materials 0.000 description 2
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 2
- OYACROKNLOSFPA-UHFFFAOYSA-N calcium;dioxido(oxo)silane Chemical compound [Ca+2].[O-][Si]([O-])=O OYACROKNLOSFPA-UHFFFAOYSA-N 0.000 description 2
- 239000010883 coal ash Substances 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 230000007246 mechanism Effects 0.000 description 2
- 238000000034 method Methods 0.000 description 2
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 239000000376 reactant Substances 0.000 description 2
- 230000000087 stabilizing effect Effects 0.000 description 2
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 1
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 239000011398 Portland cement Substances 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 230000000996 additive effect Effects 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- WNROFYMDJYEPJX-UHFFFAOYSA-K aluminium hydroxide Chemical compound [OH-].[OH-].[OH-].[Al+3] WNROFYMDJYEPJX-UHFFFAOYSA-K 0.000 description 1
- 229910052785 arsenic Inorganic materials 0.000 description 1
- RQNWIZPPADIBDY-UHFFFAOYSA-N arsenic atom Chemical compound [As] RQNWIZPPADIBDY-UHFFFAOYSA-N 0.000 description 1
- 239000012752 auxiliary agent Substances 0.000 description 1
- 239000007844 bleaching agent Substances 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- JOPOVCBBYLSVDA-UHFFFAOYSA-N chromium(6+) Chemical compound [Cr+6] JOPOVCBBYLSVDA-UHFFFAOYSA-N 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 239000000084 colloidal system Substances 0.000 description 1
- 238000005056 compaction Methods 0.000 description 1
- 238000013329 compounding Methods 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 229940079593 drug Drugs 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 230000002708 enhancing effect Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 230000003301 hydrolyzing effect Effects 0.000 description 1
- 230000002452 interceptive effect Effects 0.000 description 1
- 238000004898 kneading Methods 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 230000009965 odorless effect Effects 0.000 description 1
- 230000008520 organization Effects 0.000 description 1
- 239000003002 pH adjusting agent Substances 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 238000006068 polycondensation reaction Methods 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 238000005096 rolling process Methods 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 229910052710 silicon Inorganic materials 0.000 description 1
- 239000010703 silicon Substances 0.000 description 1
- 229910000029 sodium carbonate Inorganic materials 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 230000006641 stabilisation Effects 0.000 description 1
- 238000011105 stabilization Methods 0.000 description 1
- 239000003381 stabilizer Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 238000010998 test method Methods 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B28/00—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
- C04B28/02—Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing hydraulic cements other than calcium sulfates
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B40/00—Processes, in general, for influencing or modifying the properties of mortars, concrete or artificial stone compositions, e.g. their setting or hardening ability
- C04B40/0028—Aspects relating to the mixing step of the mortar preparation
- C04B40/0039—Premixtures of ingredients
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2111/00—Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
- C04B2111/00474—Uses not provided for elsewhere in C04B2111/00
- C04B2111/00732—Uses not provided for elsewhere in C04B2111/00 for soil stabilisation
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Abstract
Description
【0001】[0001]
【産業上の利用分野】この発明は、軟弱地盤の改良、ヘ
ドロ等の有機質汚泥又は有毒産廃物の封じ込め等に利用
できる固化剤に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a solidifying agent which can be used for improving soft ground and containing organic sludge such as sludge or toxic industrial waste.
【0002】[0002]
【従来の技術】現在、固化剤の主流は、セメント系であ
り、有機質土壌その他特殊用途に石灰系固化剤が使用さ
れるがアルカリ流出等の問題が解消されていないため一
般には殆ど使用されないのが現状である。2. Description of the Related Art Currently, the mainstream of solidifying agents is cement-based, and lime-based solidifying agents are used for organic soil and other special purposes, but they are not generally used because problems such as alkali outflow have not been solved. Is the current situation.
【0003】[0003]
【解決しようとする問題点】本発明は無機質土壌は勿
論、有機質土壌にも適用でき、しかも土壌中の水分を急
速に吸収し、急速な硬化反応と共に固化対象物を高強度
化でき、軽量で安価な粉末状処理剤を提供するものであ
る。更に処理土壌のPHを大きく変動させない固化剤を
提供するものである。[Problems to be Solved] The present invention can be applied not only to inorganic soils but also to organic soils, and moreover, it can rapidly absorb moisture in the soil, increase the strength of an object to be solidified with a rapid hardening reaction, and be lightweight. An inexpensive powdery treatment agent is provided. Further, the present invention provides a solidifying agent that does not significantly change the pH of treated soil.
【0004】[0004]
【解決手段】本発明は、フライアッシュ(石炭灰)又は
塩素系漂白剤を使用していない製紙工程から排出される
製紙パルプの焼却灰(PS灰)の自硬性を利用し、固化
反応によりエトリンガイトとCSH(ケイ酸カルシウム
水和物)を生成させるための反応助剤としてアルミニウ
ム塩、カルシウム化合物、アルカリ金属炭酸塩及びシリ
カヒューム等、更に酸化チタンを添加してなるものであ
って土壌との接触による水和反応の初期段階における水
分吸収と同時に有機物を取込み、その後にセメント成分
による固化を進行せしめ最終的にポゾラン反応に導くも
のである。本発明固化剤は硫酸アルミニウム5〜30重
量部、カルシウム塩10〜50重量部、アルカリ金属炭
酸塩0.1〜10重量部、シリカ又はシリカヒューム1
0〜20重量部からなる配合物(A1)10〜30重量
部に対し、フライアッシュ又はPS灰40〜90重量部
とセメント10〜60重量部からなる配合物(B)を8
0〜90重量部の割合で混合してなるものであって、こ
れを被処理地域に散布し又は固化対象物に添加して撹拌
することによって固化反応を生起させるものである。ま
た、配合物(A1)に酸化チタン3〜15重量部を添加
した配合物(A2)を用いると土壌中の有害物質の除去
が増進される効果がある。The present invention utilizes the self-hardening property of fly ash (coal ash) or incineration ash (PS ash) of papermaking pulp discharged from a papermaking process that does not use a chlorine-based bleaching agent, and uses ettringite by a solidification reaction. And aluminum oxide, calcium compound, alkali metal carbonate, silica fume, etc., as a reaction aid for producing CSH (calcium silicate hydrate), and titanium oxide, and contact with soil At the same time as absorbing water in the initial stage of the hydration reaction, the organic matter is taken in, and thereafter the solidification by the cement component proceeds to eventually lead to the pozzolanic reaction. The solidifying agent of the present invention is 5 to 30 parts by weight of aluminum sulfate, 10 to 50 parts by weight of calcium salt, 0.1 to 10 parts by weight of alkali metal carbonate, silica or silica fume 1.
8 to 10 parts by weight of compound (A1) consisting of 0 to 20 parts by weight of compound (B) consisting of 40 to 90 parts by weight of fly ash or PS ash and 10 to 60 parts by weight of cement.
The mixture is mixed in an amount of 0 to 90 parts by weight, and the solidification reaction is caused by being sprayed on the treated area or added to the object to be solidified and stirred. Further, the use of the compound (A2) in which 3 to 15 parts by weight of titanium oxide is added to the compound (A1) has the effect of enhancing the removal of harmful substances in the soil.
【0005】土壌等に対して散布又は撹拌されると本発
明固化剤においてフライアッシュ及びPS灰はポーラス
表面によって土壌中の水分を急速に吸収すると共にそれ
自体に含有する石膏成分、酸化アルミニウム、酸化ケイ
素等によって硬化を促進させる。本発明において添加さ
れているカルシウム化合物は上記フライアッシュ等が本
来的に具備する硬化反応を一層増進させるためであり配
合添加量は上記範囲内において実験的に決定される。シ
リカ系成分も同様の目的で配合されるものであるが、単
に硬化成分の不足を補うばかりでなく硬化生成反応物で
あるエトリンガイドとCSH(ケイ酸カルシウム水和
物)の生成に寄与するものである。エトリンガイトは3
CaO・Al2O3・3CaSO4・32H2Oなる化学式
にみられるようにその生成に当って水和反応により多量
の水が消費される。またCSHも多量の水分を消費す
る。同時にこれらの水和反応により周囲の有機物を取込
んで行く。これらの生成反応は有機物の存在下でも進行
するため本発明固化剤は有機系土壌でも無機系土壌にも
有効に作用するのである。更に、シリカヒュームはアモ
ルファスであるため反応開始と同時に激しく結晶化す
る。このとき同時に存在しているセメントから生成した
セメント系硬化反応物と相互干渉的に影響し合ってシリ
カ質の強硬度結晶体となる。また、硫酸アルミニウムは
加水分解して水酸化アルミニウムのコロイドを生成する
過程においてアルミニウムの重縮合イオンが高分子体と
して生成し土壌粒子を吸着しながら凝結する。この凝結
作用は各添加薬剤及び前記フライアッシュの物理的吸水
作用と相俟って本剤に早強性と初期材令強度の発現に貢
献する。更に、硫酸アルミニウムは、全体としてアルカ
リ反応として進行する固化反応を非アルカリ領域におい
ても進行させ、対象土がアルカリ性化するのを防ぐ効果
がある。またアルカリ炭酸塩はアッシュ成分の一部をな
すシリカ質等から反応性イオンSi4+、Al3+の溶出を
促進して固化反応に関与する。上記各薬剤は多角的に複
雑に関係し合って種々の固化反応物を生成し、セメント
はこれら固化反応物の凝固材として作用する。セメント
はポルトランドセメント又は早強セメントがよい。この
他、同時に添加される酸化チタン及び酸化シリカは、フ
ライアッシュ等に僅かながら含まれている物質である
が、酸化チタンを追加添加することによって対象土中の
重金属類、有機物、農業等の分解除去が促進されること
が確認されている。なお、この反応機序についての詳細
は明らかでないが、太陽光の照射によって起る触媒作用
が関与しているものと推測される。When sprayed or agitated on soil or the like, in the solidifying agent of the present invention, fly ash and PS ash rapidly absorb moisture in the soil by the porous surface and also contain gypsum component, aluminum oxide, oxide contained in itself. Cure is accelerated by silicon or the like. The calcium compound added in the present invention is to further enhance the hardening reaction inherently possessed by the fly ash and the like, and the addition amount of the compound is experimentally determined within the above range. Silica-based components are also mixed for the same purpose, but not only supplement the lack of curing components, but also contribute to the formation of curing reaction products, ethrin guide and CSH (calcium silicate hydrate). It is a thing. Ettringite is 3
As shown in the chemical formula CaO.Al 2 O 3 .3CaSO 4 .32H 2 O, a large amount of water is consumed by the hydration reaction in the formation thereof. CSH also consumes a large amount of water. At the same time, the surrounding organic substances are taken in by these hydration reactions. Since these formation reactions proceed even in the presence of organic matter, the solidifying agent of the present invention effectively acts on both organic soil and inorganic soil. Further, since silica fume is amorphous, it crystallizes violently at the same time when the reaction starts. At this time, the cement-based hardening reaction product produced from the cement that is present at the same time interacts with each other in an interfering manner to form a siliceous strong hardness crystal. In the process of hydrolyzing aluminum sulfate to form a colloid of aluminum hydroxide, polycondensation ions of aluminum are produced as a polymer and are condensed while adsorbing soil particles. This coagulation action, together with the physical water absorption action of each additive and the fly ash, contributes to the development of early strength and early age strength of the present drug. Further, aluminum sulfate has the effect of causing the solidification reaction, which proceeds as an alkali reaction as a whole, to proceed even in the non-alkali region, and to prevent the target soil from becoming alkaline. Further, the alkali carbonate participates in the solidification reaction by promoting the elution of the reactive ions Si 4+ and Al 3+ from the siliceous material forming a part of the ash component. Each of the above-mentioned agents is diversified and complicatedly related to each other to form various solidification reactants, and the cement acts as a solidifying material for these solidification reactants. The cement is preferably Portland cement or early strength cement. In addition to this, titanium oxide and silica oxide added at the same time are substances contained in fly ash and the like, but the addition of titanium oxide causes decomposition of heavy metals, organic matter, agriculture, etc. in the target soil. It has been confirmed that removal is facilitated. Although the details of this reaction mechanism are not clear, it is presumed that the catalytic action caused by the irradiation of sunlight is involved.
【0006】[0006]
配合物(A1) 硫酸アルミニウム 10重量部 硫酸カルシウム 10重量部 炭酸ナトリウム 0.1重量部 シリカヒューム 10重量部 配合物(B) PS灰 70重量部 早強セメント 20重量部 上記混合割合の配合物(A1)の10重量部に対して配
合物(B)90重量部を混合して調整とした。上記割合
での配合物全体の成分分析結果は表1のようであった。Formulation (A1) Aluminum sulfate 10 parts by weight Calcium sulfate 10 parts by weight Sodium carbonate 0.1 parts by weight Silica fume 10 parts by weight Formulation (B) PS ash 70 parts by weight Early strength cement 20 parts by weight 90 parts by weight of the compound (B) was mixed with 10 parts by weight of A1) to prepare the mixture. Table 1 shows the results of component analysis of the entire formulation at the above ratio.
【0007】[0007]
【表1】 なお、ヒ素、鉛、カドミウム、六価クロムその他重金属
類の分析値はいずれも分析検出限界以下であった。[Table 1] The analytical values of arsenic, lead, cadmium, hexavalent chromium and other heavy metals were all below the analytical detection limit.
【0008】[0008]
【試験例1】 新川汚泥土質改良に伴う一軸圧縮試験(静岡県浜松市新
川より採取汚泥) 供試体作成日:平成5年3月19日 試験日 :平成5年3月26日(7日養生) 試験機関 :株式会社松浦工事事務所 試験方法 :有機質汚泥である新川の川底堆積汚泥2
00gを採取し、実施例安定処理混合物((A1)及び
(B))と、比較のためにセメント系固化剤による安定
処理混合物の同重量%混合した供試体を作成して一軸圧
縮試験を行った。 同量混合(100g)ではあるが、実施例固化剤に関し
ては、その配合比の異なるものを(E1),(E2),
(E3)の3種類作成し(表2)、またセメント系に対
してはK1,K2,K3として、各々別のメーカーの固
化剤を使用した(表3)。 K1:M社製高有機質用セメント系固化剤 K2:M社製セメント系固化剤 K3:O社製セメント系固化剤[Test Example 1] Shinkawa sludge uniaxial compression test for soil improvement (sludge collected from Shinkawa, Hamamatsu City, Shizuoka Prefecture) Specimen creation date: March 19, 1993 Test date: March 26, 1993 (7 days curing ) Testing organization: Matsuura Construction Office Co., Ltd. Testing method: Shinkawa river bottom sediment sludge, which is organic sludge 2
A uniaxial compression test was carried out by collecting 00 g and preparing a test sample in which the same amounts by weight of the stabilizing treatment mixture of Examples ((A1) and (B)) and the stabilizing treatment mixture with the cement-based solidifying agent were mixed for comparison. It was Although mixed in the same amount (100 g), with respect to the solidifying agents of Examples, those having different compounding ratios (E1), (E2),
Three types of (E3) were prepared (Table 2), and for the cement type, solidifying agents of different manufacturers were used as K1, K2 and K3 (Table 3). K1: High-organic cement-based solidifying agent manufactured by M company K2: Cement-based solidifying agent manufactured by M company K3: Cement-based solidifying agent manufactured by O company
【0009】[0009]
【表2】実施例安定処理物の一軸圧縮試験 汚
泥200g [Table 2] Example Uniaxial compression test of stabilized products Sludge 200 g
【0010】[0010]
【表3】セメント安定処理物の一軸圧縮試験 汚
泥200g [Table 3] Uniaxial compression test for cement stabilized products Sludge 200g
【0011】[0011]
【考察】本発明固化剤は(E1),(E2),(E3)
共に充分な強度を発現している。通常有機汚泥の処理の
場合、迅速な搬出を求める物が殆どであり、上記試験結
果程の強度は要しないから使用量はセメント系固化剤の
使用量より少量で充分であることが判る。今回、供試体
の作成さえもできなかったセメント系のK2,K3は別
として、破砕試験にまで至った供試体のうち、、最も強
度の低かった(E2)の供試体でも、対象土が浚渫に際
して排される有機汚泥であることを考慮すれば、発現強
度の1/3程度の強度があれば充分である。また、この
中で低コストの順でランク付けすれば、(E2),(E
1),(E3),K1となる。通常の有機汚泥処理に対
する目的強度からすれば、本試験で添加された量に対し
て、(E2)ならば50%、(E1)ならば40%、
(E3)ならば30%程度の添加量で充分に目的強度が
達成される。上記の実験においては(E3)が最も安価
であると判断され易いが、実際に即効性が要求される現
場においては、トータルコスト的にも(E2)が最適で
あると言える。K1はセメント系ながら充分に強度を発
現しているが、高有機質用特殊固化剤であるから当然の
結果である。本発明固化剤(E3)は、前記高有機質用
のK1よりも高い強度を得ている。(E1),(E
2),(E3)のうち(E3)が最も大きな強度を得た
のは、7日養生によるテストピース破砕試験に起因する
ものであり、丁度エトリンガイト、CSHの生成が完了
し、中期強度を支配するセメント水和物の強度反応エリ
アにあるためであると考えられる。[Discussion] The solidifying agent of the present invention is (E1), (E2), (E3)
Both exhibit sufficient strength. Usually, in the case of the treatment of organic sludge, most of them are required to be carried out promptly, and the strength of the above test results is not required, so it can be understood that the amount used is smaller than the amount used for the cement-based solidifying agent. This time, apart from cement-based K2 and K3, which were not able to even prepare specimens, of the specimens that had reached the crushing test, even the specimen of the lowest strength (E2), the target soil was dredged. Considering that the organic sludge is discharged at that time, the strength of about 1/3 of the expression strength is sufficient. Moreover, if the ranking is made in order of low cost among these, (E2), (E
1), (E3), and K1. From the target strength for ordinary organic sludge treatment, 50% for (E2), 40% for (E1), relative to the amount added in this test,
In the case of (E3), the target strength is sufficiently achieved with an addition amount of about 30%. In the above experiment, (E3) is likely to be judged to be the cheapest, but it can be said that (E2) is optimal in terms of total cost in the field where immediate effect is actually required. Although K1 is a cement type, it exhibits sufficient strength, which is a natural result because it is a special solidifying agent for high organic matter. The solidifying agent (E3) of the present invention has higher strength than K1 for high organic matter. (E1), (E
(E3) of 2) and (E3) obtained the highest strength because it was due to the test piece crushing test by 7-day curing, and the generation of ettringite and CSH was just completed, and the medium-term strength was controlled. It is considered that this is because it is in the strength reaction area of cement hydrate.
【0012】[0012]
【試験例2】固化剤として実施例の配合物(A1)に酸
化チタン10重量部を添加した配合物(A2)を使用し
た。 ヘドロ埋設地表層改良試験 試験場所:北海道恵庭市 玉川組ヘドロ埋設地 試験日時:平成5年5月8日:平板載荷試験は5月12
日 現場状況:ボーリング試験を現場の任意3カ所で行った
ところ、最浅9m、最深13mまでN値がゼロであっ
た。 試験方法:現場で5m×10mを仕切り、表層から深度
1.5mを改質。上記固化剤配合量は、改質土量の3.
5重量%。使用機械は通常のユンボ機に、混練を満遍な
く行うため、特殊アタッチメントとしてバケットスタビ
ライザーを装着使用。採取データとして平板載荷試験を
施工範囲内2カ所で行った(表4、表5)。Test Example 2 As a solidifying agent, a compound (A2) obtained by adding 10 parts by weight of titanium oxide to the compound (A1) of the example was used. Sludge burial surface surface improvement test Test place: Eniwa City, Hokkaido Tamagawa-gumi Sludge burial site Test date: May 8, 1993: Plate loading test May 12
Daily field situation: When a boring test was conducted at three arbitrary sites, the N value was zero up to the shallowest 9 m and the deepest 13 m. Test method: 5 m x 10 m is partitioned on site and a depth of 1.5 m is modified from the surface. The solidifying agent content is 3.
5% by weight. The machine used is a normal Yumbo machine, and a bucket stabilizer is used as a special attachment to perform kneading evenly. A flat plate loading test was carried out at two locations within the construction range as collected data (Tables 4 and 5).
【0013】[0013]
【表4】平板載荷試験結果 測定場所:No.1 測定月日:平成5年5月12日 測定者 :松尾 努(玉川組土質試験室) 載荷板直径30cm 載荷板面積706.5cm2 土壌改良 平成5年5月8日施工 18:00完了[Table 4] Plate loading test results Measurement location: No. 1 Date of measurement: May 12, 1993 Measurer: Tsutomu Matsuo (Tamagawa Gumi Laboratory) Loading plate diameter 30 cm Loading plate area 706.5 cm 2 Soil improvement Construction on May 8, 1993 Completed 18:00
【0014】[0014]
【表5】測定場所:No.2 測定月日:平成5年5月12日 測定者 :松尾 努 載荷板直径30cm 載荷板面積706.5cm2 [Table 5] Measurement location: No. 2 Date of measurement: May 12, 1993 Measurer: Tsutomu Matsuo Loading plate diameter 30 cm Loading plate area 706.5 cm 2
【0015】上記表4及び表5の沈下量と全荷重との関
係をグラフ化すると図1及び図2のようになる。The relationship between the subsidence amount and the total load in Tables 4 and 5 is graphed as shown in FIGS. 1 and 2.
【0016】[0016]
【考察】施工地は9m以上のヘドロ埋設地であり、現場
状況は底無し沼的な状況であった。処理前には重機類の
侵入など考えられない場所であったが、本発明固化剤を
散布、撹拌しながら17t重量のユンボが進行できた。
転圧処理完了後、4日後に一部を再掘削したところ、
1.5mの深度で固化処理した場所が2m〜2.5m前
後まで固化状態が確認できた。これはフライアッシュが
水分を吸水すると同時に、毛細管現象的に下部の水分ま
で吸水固化したものと考えられる。同時にシリカヒュー
ムのようなアモルファス成分が、能動的に固化状況を進
展させることに貢献していると思われる。上記固化処理
により得た「平板載荷試験データ」は、一級国道の路盤
強度を凌駕する結果であった。[Discussion] The construction site was a sled burial site with a length of 9 m or more, and the site condition was a bottomless swamp. Before the treatment, it was a place where it was unlikely that heavy machinery would invade, but a 17 ton weight Yumbo was able to proceed while spraying and stirring the solidifying agent of the present invention.
After excavating a part of it 4 days after the completion of rolling compaction,
The solidified state could be confirmed up to around 2 m to 2.5 m at the solidified location at a depth of 1.5 m. It is considered that this is because the fly ash absorbed water and at the same time, the water in the lower part absorbed and solidified due to a capillary phenomenon. At the same time, it seems that an amorphous component such as silica fume actively contributes to the progress of solidification. The “plate loading test data” obtained by the solidification treatment was a result that exceeded the roadbed strength of a first-class national highway.
【0017】[0017]
【効果】本発明固化処理剤は、有機の存在に殆ど影響を
受けないエトリンガイト及びCSHを硬化反応生成物と
して生成するため、無機質土壌には勿論のこと、有機質
土壌に対しても充分にその固化反応を発揮する。また土
壌の有機、無機成分に殆ど影響を受けないため、従来の
セメント系の様に軟弱地盤改良工事中に予測以上の有機
物の存在によって、その必要量が飛躍的に増大してしま
うことがなく、含水比さえ確定させておけば工事計画時
に算定された必要量を越えるおそれはない。更に本固化
剤中に含まれるセメント量が比較的少量であり、且つ硫
酸アルミニウム等が固化反応助剤として作用すると同時
にPH調整剤としても機能するため、安定処理後の土壌
PH値を中性域に維持することができ、環境保全上極め
て望ましい状態になる。本発明固化剤中の石炭灰や製紙
焼却灰等は産廃物の一種であるからその処理問題共々に
解決ができ、廃棄物のリサイクルとして有効で、コスト
も安価になる。この他、主成分である灰分が、対象土中
に含まれる水分を急速に吸水するので反応の即効性があ
り、目的強度、目的含水比に到達するための投入量、及
び時間が少なくて済む利点がある。一般に処理対象汚泥
中に含まれる臭気や有害物質などは、その殆どが汚泥中
の水分に溶け込む様な状態で存在している。然るに従来
の各種固化剤は化学反応によって水分を取込む形態であ
ったり、発水させる形態であったため、本来の汚泥の悪
臭に対し無力であったり、更に悪いことに一層の異臭を
発生させたりするという問題があったが、本固化剤の固
化メカニズムにあっては、それらの水分は灰のポーラス
面に吸水され、その表面をエトリンガイトやCSH等の
硬化反応生成物が、コーティングする様に生成されるた
め、固化反応の進展と共に臭気は軽減され、固化反応終
了時には全く無臭となる。同様に重金属イオン類等の有
害物質等もアッシュ成分内部に封じ込められるため、再
溶出しない。加えて従来品はおしなべて比重が1以上で
重いが、本発明固化剤はアッシュ分とシリカヒューム等
を多量に含むために軽比重である。また特に浚渫汚泥等
に関しては迅速な搬出が求められる物であるが、本発明
固化剤は比重が軽いので混和後の搬出土壌の重量の軽減
にも役立ちコストを削減できる。[Effect] Since the solidifying agent of the present invention produces ettringite and CSH, which are hardly affected by the presence of organic matter, as hardening reaction products, the solidification agent is sufficiently solidified not only on inorganic soil but also on organic soil. Exert a reaction. In addition, since the organic and inorganic components of the soil are hardly affected, the required amount will not dramatically increase due to the presence of organic matter more than expected during the soft ground improvement work like the conventional cement type. As long as the water content ratio is fixed, there is no risk of exceeding the required amount calculated at the time of construction planning. Furthermore, since the amount of cement contained in the present solidifying agent is relatively small, and aluminum sulfate and the like act as a solidification reaction auxiliary agent and at the same time also function as a PH adjusting agent, the soil PH value after stabilization is adjusted to a neutral range. It can be maintained at a high level, which is extremely desirable for environmental protection. Coal ash, paper ash, and the like in the solidifying agent of the present invention are a type of industrial waste, and therefore they can be solved together with their processing problems, are effective as waste recycling, and are inexpensive. In addition, ash, which is the main component, absorbs water contained in the target soil rapidly, which has immediate effect on the reaction, and requires less amount of time and amount of input to reach the target strength and target water content ratio. There are advantages. Generally, most of odors and harmful substances contained in the sludge to be treated exist in a state of being dissolved in water in the sludge. However, since various conventional solidifying agents have a form of taking in water by a chemical reaction or a form of producing water, they are ineffective against the original bad odor of sludge, or worse, they generate a strange odor. However, according to the solidification mechanism of the solidifying agent, the water content is absorbed by the porous surface of the ash, and the surface is coated with the hardening reaction products such as ettringite and CSH. Therefore, the odor is reduced with the progress of the solidification reaction, and becomes completely odorless at the end of the solidification reaction. Similarly, harmful substances such as heavy metal ions are also contained inside the ash component and do not elute again. In addition, the conventional products have a specific gravity of 1 or more as a whole, but the solidifying agent of the present invention has a light specific gravity because it contains a large amount of ash and silica fume. In particular, dredging sludge and the like are required to be quickly carried out, but since the solidifying agent of the present invention has a low specific gravity, it can also help reduce the weight of the carried-out soil after admixture and reduce costs.
【図1】試験例2の平板載荷試験No.1の沈下量と荷
重強度の関係を示すグラフ。1 is a flat plate loading test No. 2 in Test Example 2. FIG. The graph which shows the amount of subsidence of 1 and the load strength.
【図2】試験例2の平板載荷試験No.2の沈下量と荷
重強度の関係を示すグラフ。2 is a flat plate loading test No. 2 in Test Example 2. FIG. The graph which shows the amount of subsidence of 2 and the relationship of load intensity.
なし None
Claims (2)
シウム塩10〜50重量部、アルカリ金属炭酸塩0.1
〜10重量部、シリカ又はシリカヒューム10〜20重
量部からなる配合物(A1)10〜30重量部に対し、
フライアッシュ又はPS灰40〜90重量部とセメント
10〜60重量部からなる配合物(B)を80〜90重
量部の割合で含む汚泥固化処理剤。1. Aluminum sulfate 5 to 30 parts by weight, calcium salt 10 to 50 parts by weight, alkali metal carbonate 0.1.
-10 parts by weight, and 10 to 30 parts by weight of the compound (A1) consisting of 10 to 20 parts by weight of silica or silica fume,
A sludge solidifying agent containing 80 to 90 parts by weight of the compound (B) consisting of 40 to 90 parts by weight of fly ash or PS ash and 10 to 60 parts by weight of cement.
シウム塩10〜50重量部、アルカリ金属炭酸塩0.1
〜10重量部、シリカ又はシリカヒューム10〜20重
量部、酸化チタン3〜15重量部からなる配合物(A
2)10〜30重量部に対し、フライアッシュ又はPS
灰40〜90重量部とセメント10〜60重量部からな
る配合物(B)を80〜90重量部の割合で含む汚泥固
化処理剤。2. An aluminum sulfate of 5 to 30 parts by weight, a calcium salt of 10 to 50 parts by weight, and an alkali metal carbonate of 0.1.
-10 parts by weight, 10 to 20 parts by weight of silica or silica fume, and 3 to 15 parts by weight of titanium oxide (A
2) 10 to 30 parts by weight of fly ash or PS
A sludge solidifying agent containing 80 to 90 parts by weight of the mixture (B) consisting of 40 to 90 parts by weight of ash and 10 to 60 parts by weight of cement.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP31596793A JPH07136693A (en) | 1993-11-22 | 1993-11-22 | Sludge solidification agent |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP31596793A JPH07136693A (en) | 1993-11-22 | 1993-11-22 | Sludge solidification agent |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH07136693A true JPH07136693A (en) | 1995-05-30 |
Family
ID=18071745
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP31596793A Pending JPH07136693A (en) | 1993-11-22 | 1993-11-22 | Sludge solidification agent |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH07136693A (en) |
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2000109832A (en) * | 1998-10-01 | 2000-04-18 | Ube Ind Ltd | Solidifying material for moisture-containing soil and improvement of solidification of moisture-containing soil |
JP2000109831A (en) * | 1998-10-01 | 2000-04-18 | Ube Ind Ltd | Solidifying material for moisture-containing soil and improvement of solidification of moisture-containing soil |
JP2003292956A (en) * | 2002-04-05 | 2003-10-15 | Daiho Constr Co Ltd | Soil-improving agent |
JP2005336232A (en) * | 2004-05-24 | 2005-12-08 | Shokudai Hanbai Kk | Soil solidification agent |
JP2006316195A (en) * | 2005-05-13 | 2006-11-24 | Daio Paper Corp | Soil-improving material |
CN107029658A (en) * | 2017-05-31 | 2017-08-11 | 济南大学 | A kind of preparation method of oil slick scavenger |
CN107555743A (en) * | 2017-10-31 | 2018-01-09 | 江苏和合环保集团有限公司 | A kind of stabilizer of Solid Waste Treatment containing heavy metal |
CN107585986A (en) * | 2017-10-30 | 2018-01-16 | 江苏和合环保集团有限公司 | A kind of heavy metal stabilizer and its application method |
-
1993
- 1993-11-22 JP JP31596793A patent/JPH07136693A/en active Pending
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2000109832A (en) * | 1998-10-01 | 2000-04-18 | Ube Ind Ltd | Solidifying material for moisture-containing soil and improvement of solidification of moisture-containing soil |
JP2000109831A (en) * | 1998-10-01 | 2000-04-18 | Ube Ind Ltd | Solidifying material for moisture-containing soil and improvement of solidification of moisture-containing soil |
JP2003292956A (en) * | 2002-04-05 | 2003-10-15 | Daiho Constr Co Ltd | Soil-improving agent |
JP2005336232A (en) * | 2004-05-24 | 2005-12-08 | Shokudai Hanbai Kk | Soil solidification agent |
JP2006316195A (en) * | 2005-05-13 | 2006-11-24 | Daio Paper Corp | Soil-improving material |
CN107029658A (en) * | 2017-05-31 | 2017-08-11 | 济南大学 | A kind of preparation method of oil slick scavenger |
CN107029658B (en) * | 2017-05-31 | 2020-01-17 | 济南大学 | Preparation method of water surface floating oil scavenger |
CN107585986A (en) * | 2017-10-30 | 2018-01-16 | 江苏和合环保集团有限公司 | A kind of heavy metal stabilizer and its application method |
CN107555743A (en) * | 2017-10-31 | 2018-01-09 | 江苏和合环保集团有限公司 | A kind of stabilizer of Solid Waste Treatment containing heavy metal |
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