JP2001300591A - Method for simply coagulating muddy material decreasing volume thereof and stabilizing the same - Google Patents

Method for simply coagulating muddy material decreasing volume thereof and stabilizing the same

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Publication number
JP2001300591A
JP2001300591A JP2000161198A JP2000161198A JP2001300591A JP 2001300591 A JP2001300591 A JP 2001300591A JP 2000161198 A JP2000161198 A JP 2000161198A JP 2000161198 A JP2000161198 A JP 2000161198A JP 2001300591 A JP2001300591 A JP 2001300591A
Authority
JP
Japan
Prior art keywords
bag
mud
muddy
hydrated
sludge
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
Application number
JP2000161198A
Other languages
Japanese (ja)
Inventor
Kazuya Yasutomi
一也 安富
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
CHOBI KK
KURIENSU KOGYO KK
Original Assignee
CHOBI KK
KURIENSU KOGYO KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by CHOBI KK, KURIENSU KOGYO KK filed Critical CHOBI KK
Priority to JP2000161198A priority Critical patent/JP2001300591A/en
Publication of JP2001300591A publication Critical patent/JP2001300591A/en
Pending legal-status Critical Current

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Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

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  • Treatment Of Sludge (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a treatment method which subjects hydrophilic muddy material such as dredged sludge, sludge and various waste sludge to coagulation treatment easily even for muddy material of high or low water content by using a simple tool/ apparatus, enables decreasing the volume in the short term by solar drying and provides hard aggregate similar to neutral sandy soil which is stable without returning to the muddy state at a low cost. SOLUTION: An active silicate sol 4b which is acidic is prepared by mixing silicate substance aqueous solution incorporated with metals of high ionization tendency which is mainly composed of bivalent iron and mineral acid. An alkaline diluted silicate substance aqueous solution 4a ad the active silicate sol 4b are added to the muddy material 3 which is charged into a bag having excellent water permeability or the muddy material 3 which is directly charged into an upper part opening type tank 1 and are stirred and mixed, thereby the muddy material 3 is made to be the neutral gel-like hydrous coagulated material. The hydrous coagulated material is temporarily hung down as it is charged in the bag, is subjected to simple dehydration, thereafter, the upper part of the bag is opened, is sun-dried, or is directly taken out of the tank and is subjected to solar drying without using the bag.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、海、河川、湖沼、池等
に推積するヘドロ、建設汚泥、側構汚泥や工場内にて発
生する各種廃水スラッジ等の親水性のよい微粒子状泥状
物等(以下、単に泥状物という)を、特に特殊な機械設
備を用いることなく、硅酸物質系凝固剤を添加混合して
泥状物を凝固し、得られた含水状凝固物の容量を縮小安
定化して、かつ、残さの取り扱いを容易にし、泥状物を
再利用し得る砂質系土砂類似形状に硬化安定させる泥状
物の簡易凝固減容安定化工法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to finely particulate mud having good hydrophilicity, such as sludge, construction sludge, side sludge, and various kinds of wastewater sludge generated in factories, which are deposited on seas, rivers, lakes, lakes and ponds. The sludge is solidified by adding and mixing a silicic substance-based coagulant without using any special mechanical equipment, and the sludge is solidified. The present invention relates to a simple solidification and volume reduction stabilization method for a mud which stabilizes its capacity, facilitates the handling of the residue, and hardens and stabilizes the mud to a sandy soil and sand-like shape that can be reused.

【0002】[0002]

【従来の技術】この種の泥状物は、高含水状態で、特異
な粘性及び流動性を有している上、時には有害重金属等
の有害物質を含み、異臭を放って環境汚染の原因となる
ために、各種泥状物を硬化、安定化することは、廃棄物
汚染を防ぎ、環境浄化のためや廃棄泥状物の再資源化の
要請から、各種の処理対処法が提案、実施されている。
2. Description of the Related Art Mud-like substances of this type have a specific viscosity and fluidity in a high water content state, and sometimes contain harmful substances such as harmful heavy metals and emit off-flavors to cause environmental pollution. Therefore, curing and stabilizing various kinds of mud is to prevent waste pollution, and various treatment measures are proposed and implemented in response to requests for environmental purification and recycling of waste mud. ing.

【0003】従来、この種の泥状物の処理方法として
は、加熱処理する方法や脱水機を用いて強制的に脱水減
容化する方法が知られている。また、高含水状態の泥状
物では、凝集剤を用いて凝集処理された泥状物を二重方
式袋に投入、吊り下げ、泥状物の自重による脱水減容化
方法や凝集分離泥状物を脱水機を用いて脱水処理する方
法や沈澱槽内にて凝集沈降させることにより、分離上澄
水を除去し、その後に天日乾燥により方法も行われてい
る。これに対して、石灰やセメント等を固化剤として使
用し、泥状物を直接固化して廃棄する方法や屋外での天
日乾燥による方法も知られている。高含水状態の泥状物
は、前述のように、分離上澄水を除去した状態で、これ
らの固化剤を使用して固化する方法も実施されている。
[0003] Conventionally, as a method for treating this kind of muddy substance, a method of performing a heat treatment or a method of forcibly reducing the volume of dehydration using a dehydrator is known. In addition, in the case of mud with high water content, the mud that has been subjected to coagulation using a coagulant is placed in a double-type bag, suspended, the method of reducing the volume of dewatering by the weight of the mud, and the method of coagulation and separation mud. A method of dehydrating a product using a dehydrator or coagulating and sedimenting in a sedimentation tank to remove separated supernatant water, followed by drying in the sun is also used. On the other hand, a method in which lime, cement, or the like is used as a solidifying agent to directly solidify and discard mud, or a method in which sunlight is dried outdoors are also known. As described above, a method of solidifying a highly watery mud using these solidifying agents with the separated supernatant water removed is also being implemented.

【0004】[0004]

【発明が解決しようとする課題】しかし、従来の技術で
述べたものにおいては、それぞれの方法について、次の
とおりの解決を要する多くの問題点がある。
However, the methods described in the prior art have many problems that require the following solutions for each method.

【0005】加熱処理による方法は、微粒子状で処理量
が多く、高含水状態になるほど加熱時間が延長され、加
熱処理するための設備及び大きな熱エネルギー源が必要
になると供に、加熱温度を所定値に維持するための設備
等が必要になり、経済性が大きく損なわれる。しかも、
余剰熱エネルギーの発生ばかりか泥状物中の有害物質の
ガス化鉱散等による環境汚染の問題を生じることとな
る。
[0005] In the method by heat treatment, the amount of treatment in the form of fine particles is large, the heating time is extended as the water content increases, the equipment for heat treatment and a large heat energy source are required, and the heating temperature is set to a predetermined value. Equipment and the like for maintaining the value are required, which greatly impairs economic efficiency. Moreover,
Not only the generation of excess heat energy, but also the problem of environmental pollution due to gasification ore dispersion of harmful substances in the muddy matter will occur.

【0006】脱水機を用いて泥状物を直接脱水処理する
方法では、高含水状態の親水性泥状物を脱水するための
複雑な機構、前処理のための装置等が必要になる。又、
脱水処理物は、固化剤によって固化された場合のように
物理的及び化学的に安定な状態でないために、水分を吸
収して、再度、泥状物化する恐れがある。さらに、泥状
物の物性によって、凝集剤を使用し、フロック形成を行
った後に脱水機によって脱水処理する場合にも、生成さ
れる処理物は物理的に安定しないために、水分を吸収し
て、再度、泥状物化する恐れがあると供に、泥状物の粘
性が増大し、脱水効率が低下したり、固液分離面が目詰
まりする恐れもある。かつ、泥状物内に釘、ガラス片、
空き缶、石、ビニール等の夾雑物が混入していると脱水
が不可能となり、夾雑物を除去するための前処理設備が
必要となる。脱水設備は概して構造が複雑で周辺機器が
多く、全体設備費が高価な上、維持費も高いわりには脱
水能力があまりよくない。
The method of directly dehydrating mud using a dehydrator requires a complicated mechanism for dehydrating hydrophilic mud having a high water content, an apparatus for pretreatment, and the like. or,
Since the dehydrated product is not in a physically and chemically stable state as in the case of being solidified by the solidifying agent, there is a possibility that the dehydrated product absorbs moisture and becomes muddy again. Furthermore, due to the physical properties of the muddy substance, even when a flocculant is used and the dewatering process is performed by a dehydrator after performing floc formation, the processed material generated is not physically stable. In addition, there is a possibility that the mud may be formed again, and the viscosity of the mud may increase, dehydration efficiency may be reduced, and the solid-liquid separation surface may be clogged. And nails, glass fragments,
If contaminants such as empty cans, stones, and vinyl are mixed, dehydration becomes impossible, and a pretreatment facility for removing the contaminants is required. The dewatering equipment generally has a complicated structure and a lot of peripheral devices, and the cost of the entire equipment is high, and the dewatering ability is not so good despite the high maintenance cost.

【0007】凝集剤を用いて凝集処理された泥状物を二
重方式袋に投入し、吊り下げ、泥状物の自重による脱水
減容化方法では、高含水状態の泥状物に対しては初期的
な水分分離としての効果が認められるが、一層の脱水減
容化を図るためには、その後の自然乾燥を待たねばなら
ず、大変な日数を要し、屋外での自然乾燥の場合では、
降雨等の場合に袋を通して浸透する水分により、再度、
泥状物化する恐れがある。しかも、低含水状態の泥状物
に対しては、凝集剤による効果が期待できないため、初
期的な水分分離としての効果も失われる。
[0007] In the method of putting the mud which has been subjected to coagulation using a coagulant into a double-type bag, suspending the mud, and reducing the volume of dewatering by the weight of the mud, the mud having a high water content is removed. Has an effect as an initial water separation, but in order to further reduce the volume of dehydration, it is necessary to wait for natural drying after that, it takes a lot of days, and in the case of natural drying outdoors Then
In the case of rain, etc., due to the moisture that penetrates through the bag,
There is a risk of mud. In addition, since the effect of the flocculant cannot be expected for muddy substances having a low water content, the effect of initial moisture separation is also lost.

【0008】凝集剤を用いて凝集分離上澄水を除去し、
その後に、天日乾燥する方法や無処理のままを直接天日
乾燥する方法も考えられるが、乾燥減要化までには非常
に長期に渡る日数が必要となるばかりか、天日乾燥中で
の降雨等では、再度、泥状物化する。この様な状況で
は、乾燥処理物を得る事ができる日数の把握が困難であ
る上、降雨時における泥状物の流出や濁水処理に対する
対策が必要となる。
[0008] The coagulation separation supernatant water is removed using a coagulant,
After that, a method of drying in the sun or a method of directly drying in the untreated state can be considered.However, it takes not only a very long time to reduce drying, but also When it rains, it becomes muddy again. In such a situation, it is difficult to determine the number of days during which the dried product can be obtained, and it is necessary to take measures against the outflow of muddy substances and the treatment of turbid water during rainfall.

【0009】低含水状態の泥状物に対して、石灰、セメ
ント等の固化剤を使用し、直接固化する方法では、混入
される固化剤の分量だけ、生成される処理物の重量、容
積が増加する事となり、減容化されない上、最終固化発
現完了までのアルカリ流出対策が必要となる。また、高
含水状態の泥状物に対しては、非常に多量の固化剤が必
要となり、経済性が損なわれる。さらに、処理物の重
量、容積が増加するために、その処理物の運搬や輸送を
容易に行うことができない。
[0009] In the method of directly solidifying mud with a low water content using a solidifying agent such as lime or cement, the weight and volume of the processed material to be produced are reduced by the amount of the solidifying agent mixed. This means that the volume will not be reduced, and it is necessary to take measures against alkali spillage until the completion of the final solidification. Further, for a mud having a high water content, a very large amount of a solidifying agent is required, which impairs economic efficiency. Further, since the weight and volume of the processed material increase, it is not easy to carry or transport the processed material.

【0010】従来の方法では、有害物質を含有する泥状
物に対しては、処理過程並びに処理後の処理物に対し
て、含有有害物質の溶出や分離された分離水に対する対
策が後工程として必要となる。
[0010] In the conventional method, as for the sludge containing harmful substances, in the treatment process and after treatment, measures for elution of the harmful substances contained and separation water separated are taken as a post-process. Required.

【0011】本発明は、従来の技術の有するこのような
問題点を解決するものであり、その目的は、泥状物を特
殊な機械設備を用いる事なく、高含水状態及び低含水状
態の泥状物であっても、短時間、短期日で、しかも確実
に物理的及び化学的に長期安定減容化した硬質団粒とす
ることを低コストで、しかも、生成される硬質団粒が安
全で様々な用途に有効使用できる泥状物の簡易凝固減容
安定化工法を提供する事を目的としている。
SUMMARY OF THE INVENTION The present invention has been made to solve the above-mentioned problems of the prior art, and it is an object of the present invention to remove a mud-like substance in a high water content state and a low water content state without using special mechanical equipment. Even in the form of solids, it is possible to produce hard aggregates that are physically and chemically stable for a long period of time in a short time, on a short day, and at low cost. The purpose of the present invention is to provide a method for stabilizing the solidification and volume reduction of mud which can be effectively used for various purposes.

【0012】[0012]

【課題を解決するための手段】上記目的を達成するため
に、本発明の簡易凝固減容安定化工法においては、上部
が開放されたタンク内に置かれた透水性のよい袋に投入
された泥状物や、上部が開放されたタンク内に直接投入
された泥状物に、イオン化傾向の大きい金属類を混入さ
せた硅酸物質水溶液と鉱酸とを混合して得られた酸性の
活性珪酸ゾルとアルカリ性の希釈硅酸物質水溶液を泥状
物に添加して撹拌混合し、この泥状物を中性の含水凝固
物とする工程と、この含水凝固物を、含水凝固物の自重
を利用する方法にて一次脱水を行い、その後に、凝固反
応作用による縮合反応に伴う含水凝固物よりの離漿反応
と、天日乾燥工程による二次脱水作用にて、容易に、短
期日で、減容された物理的、化学的に安定した中性域で
の再泥化しない砂質系土砂に類似する硬質団粒を生成せ
しめる工程とを包含したものである。
In order to achieve the above object, in the method for stabilizing solidification and volume reduction according to the present invention, it is put into a bag having good water permeability placed in a tank having an open top. Acidic activity obtained by mixing a silicic acid aqueous solution containing a highly ionizable metal and a mineral acid with a muddy substance or a muddy substance directly charged into a tank with an open top. A step of adding a silicic acid sol and an aqueous solution of an alkaline diluted silicic acid substance to a mud and stirring and mixing the mud to a neutral hydrated coagulate. Perform primary dehydration by the method used, and then, by the dehydration reaction from the hydrated coagulate accompanying the condensation reaction by the coagulation reaction and the secondary dehydration by the solar drying step, easily, in a short time, Reduced volume of physically and chemically stable neutralized non-remudified sand In which it was included the step of allowed to generate a hard crumb similar to system earth and sand.

【0013】本発明が上記の如く優れた特徴をもつの
は、酸性の活性硅酸ゾルとアルカリ性の希釈硅酸物質水
溶液を泥状物に添加し、撹拌混合してやることによっ
て、硅酸物質を中和することにより調整される硅酸は、
活性化学種であり、シラノール縮合反応及び双極子相互
作用により架橋し、硬化する。この事が泥状物凝結剤と
して硅酸ゾルを有効ならしめ、泥状物を中性の含水凝固
物とする。
The present invention has excellent characteristics as described above because an acidic active silicate sol and an alkaline aqueous solution of a diluted silicate substance are added to a slurry, and the mixture is stirred and mixed. The silicic acid adjusted by summing
It is an active species that crosslinks and cures through silanol condensation reactions and dipole interactions. This makes the silica sol effective as a mud coagulant and turns the mud into a neutral hydrated coagulate.

【0014】この含水凝固物は減容性があり、物理的及
び化学的に安定している上、シロキサン結合による三次
元網目構造によって有害物質をも溶出しにくい状態とな
り、環境に悪影響のない良好な凝固物である。また、こ
の凝固物は物理的及び化学的に長期安定化されているた
め、凍結や加熱による劣化がなく、降雨等によっても、
再度、泥状化する恐れがない。
This water-containing coagulated material has a volume-reducing property, is physically and chemically stable, and has a three-dimensional network structure formed by siloxane bonds, so that harmful substances are hardly eluted. Is a solidified product. In addition, since this coagulated material is physically and chemically stabilized for a long period of time, it does not deteriorate due to freezing or heating, and even when it rains,
Again, there is no danger of muddy.

【0015】この含水凝固物は、凝固後の時間経過とと
もに、シラノール縮合を促進し、三次元網目構造が一層
発達し、シロキサン結合の切断も並発して安定な構造の
硅酸ポリマーへと成長し、泥状物粒子を強力に包蔵固結
する。これらの反応過程において、含水凝固物中の水分
を徐々に離漿水として排出し、凝固物自らが減容する性
質を合わせ持っている。また、凝固構造は離漿水中への
有害物質が溶出しにくい状態になっている。
The hydrated coagulum promotes silanol condensation with the lapse of time after the coagulation, further develops a three-dimensional network structure, breaks siloxane bonds, and grows into a silicic acid polymer having a stable structure. , Contains and solidifies mud particles. In these reaction processes, the water in the hydrated coagulate is gradually discharged as syneresis water, and the coagulate itself has the property of reducing its volume. Further, the coagulated structure is in a state where harmful substances are hardly eluted into syneresis water.

【0016】泥状物が高含水状態、低含水状態にかかわ
らず活性硅酸ゾルと希釈硅酸物質を添加し、撹拌混合を
行った結果、PHが中性になると凝固活動を開始するた
め、短時間でゲル状の中性含水凝固物とされる。また、
悪臭を持つ泥状物に対しても、凝固物は中性域で処理さ
れる事による消臭効果に加え、泥状物中での代表的な臭
気ガスとされるアンモニア臭と硫化水素臭は、泥状物に
添加される活性硅酸ゾルによりアンモニア臭は硫酸アン
モニウムとして固定され、硫化水素臭は硅酸物質水溶液
に混入された二価鉄を中心としたイオン化傾向の大きい
金属類により硫化鉄となり、中性域処理による消臭効果
と合わせ、大きな消臭効果をも合わせ持っている。
Regardless of whether the mud is high or low water content, the active silicate sol and the diluted silicate material are added, and the mixture is stirred and mixed. As a result, when the PH becomes neutral, the coagulation activity starts. It becomes a gel-like neutral hydrated coagulated product in a short time. Also,
Even for muddy substances with bad odor, the coagulated matter has a deodorizing effect by being treated in the neutral region, and the ammonia odor and hydrogen sulfide odor, which are typical odor gases in the muddy substance, The ammonia odor is fixed as ammonium sulfate by the activated silica sol added to the mud, and the hydrogen sulfide odor is converted to iron sulfide by metals with a high ionization tendency, mainly ferrous iron mixed in the aqueous solution of silica. In addition to the deodorant effect of the neutral region treatment, it also has a large deodorant effect.

【0017】タンク内に置かれる袋は、麻布、レーヨン
綿の不織布とナイロンストッキング用布を用いているた
めに、非常に透水性に優れている上、レーヨン綿は1.
5〜2mmの厚みを有しており、ランダムに重なりあっ
たレーヨン綿は櫛状のピンでついて麻布に絡み付ける工
程で加工されている布で、レーヨンの繊維間の隙間が透
水の役目をしているために孔がない状態にあり、ナイロ
ンストッキング用布を併用する事による液晶濾過効果と
合わせ、泥状物中の微粒子状固形分を通すことはない。
また、麻布はレーヨン綿を補強する役割を有しており、
この不織布の引っ張り強度は6.3kgf/cmを有
する。
The bag placed in the tank is made of a nonwoven fabric of linen cloth and rayon cotton and a cloth for nylon stocking, so that it is extremely excellent in water permeability.
The rayon cotton, which has a thickness of 5 to 2 mm and is randomly overlapped, is a cloth processed in a process of being entangled with linen with a comb-shaped pin, and the gap between the fibers of the rayon serves as a water permeator. Because of this, there is no hole, and together with the liquid crystal filtration effect of using a nylon stocking cloth together, the fine solid matter in the mud does not pass through.
Azabu has the role of reinforcing rayon cotton,
This nonwoven fabric has a tensile strength of 6.3 kgf / cm 2 .

【0018】上記の袋は、袋状に縫製されたものではな
く、円形の一枚布で、その円外周部に紐が通る状態にな
っており、紐が通されている。この紐を絞る事によって
袋状になり、絞りを暖めると平坦な円形の一枚布にな
る。
The above bag is not sewn in a bag shape, but is made of a single piece of circular cloth, with a string passing through the outer periphery of the circle, and the string is passed through. By squeezing the string, it becomes a bag-like shape, and when the squeeze is warmed, it becomes a single flat circular cloth.

【0019】この円形の布を容器内に沿って配する事に
より、布製の容器となって、泥状物を投入した場合も形
状を崩す事なく、泥状物を受け入れる事が出来る。又、
容器は1つでも、この円形の布を取替える事により、泥
状物の受け入れはスムーズに順次実施できる。
By arranging the circular cloth along the inside of the container, the container becomes a cloth container and can receive the mud without losing its shape even when the mud is introduced. or,
By replacing this circular cloth even with one container, the receiving of mud can be smoothly and sequentially performed.

【0020】前述の含水凝固物をタンク内に沿って配し
た袋とともに取り出し、吊り下げる事によって、凝固物
の自重を外力とした静圧脱水が行われ、相当量の水分を
急激に排出することができ、一次脱水としての役割を持
つ。この吊り下げ時間は3〜4時間で、その間に凝固物
中ではシロキサン結合による三次元網目構造の一層の発
達をなすことになる。
The above-mentioned hydrated coagulum is taken out together with a bag arranged along the tank and suspended, whereby static pressure dehydration is performed using the own weight of the coagulate as an external force, and a considerable amount of water is rapidly discharged. Can play a role as primary dehydration. The suspension time is 3 to 4 hours, during which time the coagulate will develop further a three-dimensional network due to siloxane bonds.

【0021】上記一次脱水後に、袋を地面上や架台上に
移動させ、袋上部を開放し、天日乾燥を行う事で短期日
に、大きく減容された中性の硬質団粒状態となる。天日
乾燥時には凝固物の縮合反応による効果も伴い、乾燥が
一層促進される。この日数は、凝固後4〜7日である。
また、これらの作業は前述の袋内で行われるため、全て
の移動が容易であり、凝固状況から目詰まりを起こしに
くいために、この袋は何度となく再使用できる。また、
40lの泥状物程度までは、全て人力で容易に作業が行
える上、凝固完了までに要する時間も15〜20分と非
常に短時間である。人力で移動が困難な泥状物量を一度
に処理する場合は、移動時の設備のみでよい事となる。
After the above-mentioned primary dehydration, the bag is moved to the ground or a gantry, the upper portion of the bag is opened, and solar drying is performed, so that a neutral hard aggregated state having a greatly reduced volume is obtained in a short period of time. . In the case of solar drying, drying is further promoted with the effect of a condensation reaction of the coagulated product. This is 4-7 days after coagulation.
In addition, since these operations are performed in the above-described bag, all the movement is easy, and the bag is hardly clogged due to the solidification state, so that the bag can be reused many times. Also,
All the work up to about 40 litters can be easily performed manually, and the time required to complete the coagulation is as short as 15 to 20 minutes. When the sludge amount that is difficult to move with human power is processed at once, only the equipment at the time of movement is sufficient.

【0022】泥状物をタンク等に直接投入し、凝固処理
を行う場合に得られた含水凝固物は、タンクより取り出
し一定の厚さに盛り上げ、屋外での天日乾燥を行うこと
によって、あまり天候に左右されることなく短期日に乾
燥され、大きく減容した砂質系土砂に類似する中性の硬
質団粒状態となる。この工程において、一定の厚さに盛
り上げることにより、その下部部分は上部凝固物の自重
を外力とした静圧脱水が行われ、相当量の水分を急激に
排出することができ、一次脱水としての役割を持つ。更
に、天日乾燥時には凝固物の縮合反応による離漿反応に
よる効果も伴い、乾燥が一層促進される。この日数は、
凝固後6〜14日である。
The hydrated coagulated material obtained when the mud is directly poured into a tank or the like and subjected to coagulation treatment is taken out of the tank, raised to a certain thickness, and dried by the sun in the outdoors. It is dried for a short period of time without being affected by the weather, and becomes a neutral hard aggregated state similar to sandy soil with greatly reduced volume. In this step, by raising to a certain thickness, the lower part is subjected to static pressure dehydration using the own weight of the upper coagulated substance as an external force, and it is possible to rapidly discharge a considerable amount of water, as a primary dehydration Have a role. Furthermore, during sun drying, drying is further promoted with the effect of a syneresis reaction due to a condensation reaction of the coagulated product. This number of days
6-14 days after coagulation.

【0023】この様に得られた処理物は、物理的及び化
学的に長期安定し、しかも環境に悪影響のない良好な硬
質団粒であり、各種用途に再利用が可能である。更に、
処理に際しての特殊な機械設備を要する事なく、容易に
処理する事が出来る。
The processed material thus obtained is a hard aggregate having good physical and chemical stability for a long period of time and no adverse effect on the environment, and can be reused for various purposes. Furthermore,
Processing can be easily performed without requiring special mechanical equipment.

【0024】[0024]

【実施例】以下に本発明の実施例を添付図面に基づき説
明すると、次の通りである。
Embodiments of the present invention will be described below with reference to the accompanying drawings.

【0025】本発明の泥状物の簡易凝固減容安定化工法
の設備として、タンク内側に透水性のよい袋を併用する
場合は、図1〜3に概略的に示される上部開放形タンク
1、透水性不織布袋2、撹拌混合棒5、一次脱水用吊り
下げ柱7、薬剤計量容器4である。泥状物の投入は、発
生源よりの直接投入やポンプ投入等の任意でよいし、薬
剤計量は自動調薬装置による薬剤、計量でもよい。ま
た、含水凝固物入りの袋の移動は、人力でも機械移動で
も任意でよい。
In the case of using a bag having good water permeability inside the tank as equipment for the method for stabilizing the solidification and volume reduction of mud according to the present invention, an open-top tank 1 schematically shown in FIGS. , A water-permeable nonwoven bag 2, a stirring and mixing rod 5, a primary dehydrating hanging column 7, and a drug measuring container 4. The introduction of the muddy substance may be arbitrary such as direct introduction from a generation source, introduction of a pump, or the like, and medicine measurement may be medicine and measurement by an automatic dispensing device. In addition, the bag containing the hydrated coagulated material may be manually or mechanically moved.

【0026】本発明の泥状物の凝固には、二価鉄を中心
としたイオン化傾向の大きい金属類を混入した硅酸物質
として硅酸ソーダ3号(この金属類の混入量は硅酸ソー
ダ3号の量に対して0.4〜1.5%の添加量)、鉱酸
として酸性硫酸ソーダを用いる。まず、硅酸ソーダ3号
を希釈水によって40〜50%の希釈硅酸ソーダ水溶液
4aを製造する。そして、この希釈硅酸ソーダ水溶液4
aを、直接、処理すべき泥状物3に添加撹拌混合すると
ともに、同量のこの希釈硅酸ソーダ水溶液に酸性硫酸ソ
ーダの10%以下の水溶液に混合して、PH1.5〜
2.2の強酸性の活性硅酸ゾル4bを調整する。調整さ
れたこの活性硅酸ゾル4bは、希釈硅酸ソーダ水溶液が
添加撹拌混合された処理すべき泥状物3に添加されて撹
拌混合される。これにより、泥状物はPH6.5〜8程
度の中性域となり、この様な状態でしばらく放置するこ
とにより、泥状物3は、短時間(10〜40分程度)で
ゲル状の中性含水凝固物となる。この酸性活性硅酸ゾル
を調節する希釈硅酸ソーダ水溶液と酸性硫酸ソーダの1
0%以下の水溶液の比率は、重量比で1:0.9〜1.
0である。
In the solidification of the mud according to the present invention, sodium silicate No. 3 containing a metal having a high ionization tendency, mainly ferric iron, is used. (Addition amount of 0.4 to 1.5% based on the amount of No. 3), and acidic sodium sulfate is used as a mineral acid. First, a 40% to 50% diluted sodium silicate aqueous solution 4a is prepared by diluting sodium silicate 3 with diluted water. And this diluted sodium silicate aqueous solution 4
a is directly added to the slurry 3 to be treated and mixed with stirring, and the same amount of this diluted aqueous sodium silicate solution is mixed with an aqueous solution of 10% or less of acidic sodium sulfate to adjust the pH to 1.5 to 1.5%.
2. Prepare a strongly acidic activated silica sol 4b of 2.2. The adjusted active silicate sol 4b is added to the slurry 3 to be treated, to which the diluted aqueous sodium silicate solution is added and mixed, and the mixture is stirred and mixed. As a result, the mud becomes a neutral region having a pH of about 6.5 to 8, and if the mud is left for a while in such a state, the mud 3 becomes gel-like in a short time (about 10 to 40 minutes). It becomes a water-containing coagulated product. A diluted sodium silicate aqueous solution and an acidic sodium sulphate
The ratio of the aqueous solution of 0% or less is 1: 0.9-1.
0.

【0027】希釈硅酸ソーダ水溶液4aは、予め泥状物
3に直接添加されて、この泥状物3中に拡散されている
ために、その後に添加される酸性活性硅酸ゾル4bは少
量であっても確実に泥状物3を中性化して含水凝固物と
することができる。このように泥状物は、希釈硅酸ソー
ダ水溶液4aが予め添加されているために、強酸性の活
性硅酸ゾル4bが添加されても含有硫化物等による臭気
の発生が抑制され、混入金属類により硫化鉄となり、一
層の抑制効果が発揮される上、含有アンモニア臭は、活
性硅酸ゾル4bにより硫酸アンモニウムとして固定され
ることから、処理後の悪臭が極端に低下する。
The diluted aqueous sodium silicate solution 4a is directly added to the slurry 3 in advance, and is diffused in the slurry 3, so that the acid active silica sol 4b to be added thereafter is a small amount. Even if it is present, the mud 3 can be surely neutralized to obtain a hydrated coagulated product. As described above, since the dilute sodium silicate aqueous solution 4a is added in advance to the mud, even when the strongly acidic active silicate sol 4b is added, generation of odor due to sulfides and the like is suppressed, and the mixed metal The compounds form iron sulfide, which exerts a further suppressing effect. Further, since the contained ammonia odor is fixed as ammonium sulfate by the active silicic acid sol 4b, the malodor after the treatment is extremely reduced.

【0028】本発明の初期の効果を発現するには、凝結
剤としての活性硅酸ゾルを処理すべき泥状物の泥質、施
工性、得られる処理物の性質、経済性、目的等に応じて
濃度、添加量が選定され、例えば、処理すべき泥状物に
対して2.5〜30%の添加量とされ、約10〜40分
間放置する。
In order to exhibit the initial effects of the present invention, the active silicic acid sol as a coagulant needs to be treated in terms of the muddy properties of the mud to be treated, the workability, the properties of the resulting treated material, economy, purpose and the like. The concentration and the amount of addition are selected accordingly, for example, the addition amount is 2.5 to 30% with respect to the mud to be treated, and the mixture is left for about 10 to 40 minutes.

【0029】泥状物中での添加薬剤の撹拌混合には、図
2の撹拌混合棒5を上下に移動反復させる事によって、
濃度の異なる泥状物と薬剤の均一な混合を容易にする。
撹拌混合棒5は風呂の湯掻き棒のような形状をする。ま
た、撹拌混合は極力上下に撹拌混合する事が要求される
ため、撹拌混合棒5以外であっても容易に上下撹拌が実
施されるものであれば、機械設備、人力撹拌の別なく用
いられる。
The stirring and mixing of the added drug in the mud is carried out by moving the stirring and mixing rod 5 in FIG.
Facilitates uniform mixing of mud with different concentrations of drug.
The stirring and mixing rod 5 has a shape like a bath scraper. In addition, since the stirring and mixing is required to be stirred and mixed as much as possible up and down, as long as the stirring and mixing can be easily performed even with a rod other than the stirring and mixing rod 5, it is used regardless of the mechanical equipment and the manual stirring. .

【0030】泥状物の凝固完了後は、容器1内透水性不
織布袋2の図5の袋とじ紐2aを絞り込む事によって、
図6のように含水凝固物6を包み込んだ袋状となる。こ
の袋を容器1より取り出し移動させる。この時、とじ紐
は移動をより容易とする。
After the solidification of the mud is completed, the bag binding string 2a shown in FIG.
As shown in FIG. 6, it becomes a bag shape enclosing the hydrated coagulated material 6. The bag is taken out of the container 1 and moved. At this time, the binding string makes the movement easier.

【0031】含水凝固物を包み込んだ透水性不織布袋2
を容器内より取り出し、図3の一次脱水用吊り下げ柱7
に取り下げる事によって、含水凝固物の重量が静圧力と
して作用し、透水性不織布袋2を固液分離面として、一
時的ではあるが、含水凝固物の脱水が有効に行われる。
この場合、凝固物中の分離が容易な水分は1〜2時間で
大部分が排出されるため、この一次脱水作業は3〜4時
間程度とする。吊り下げ時間は、より短くともより長く
とも、最終効果にはあまり影響される事がない。この間
に、凝固物でのシロキサン結合により三次元網目構造
は、一層の発達が促進される。
Water-permeable nonwoven bag 2 wrapped with hydrated coagulated material
Is taken out of the container, and the suspension column 7 for primary dehydration in FIG.
The weight of the hydrated coagulated material acts as a static pressure, and the dewatering of the hydrated coagulated material is performed temporarily, although temporarily, using the water-permeable nonwoven fabric bag as a solid-liquid separation surface.
In this case, most of the easily separated water in the coagulated matter is discharged in 1 to 2 hours, so this primary dehydration operation is performed in about 3 to 4 hours. The suspension time, whether shorter or longer, is less affected by the end effect. During this time, the siloxane bond in the coagulate promotes further development of the three-dimensional network structure.

【0032】一次脱水後、袋を移動させ、図4のように
地上面又は架台上に、袋上部とじ紐2aを暖め、全開放
状態として天日乾燥を行い放置する。この場合、天日に
よる水分の蒸発、通気性とともに、凝固に伴う縮合反応
により一層の凝固物中の水分排出を助長することにな
る。又、凝固物は物理的及び化学的に非常に安定してい
るため、天日乾燥途上での降雨によっても固形分の流出
や再度、泥状化する心配がない上、外気温度の極端な低
下での凍結にも劣化する心配もない。
After the primary dehydration, the bag is moved, the binding cord 2a at the top of the bag is warmed on the ground surface or a gantry as shown in FIG. In this case, in addition to evaporation and air permeability of moisture due to sunlight, a condensation reaction accompanying solidification promotes further drainage of moisture in the solidified product. In addition, since the coagulated material is extremely stable physically and chemically, there is no need to worry about solids flowing out and muddy again due to rainfall in the course of drying in the sun, and extremely low outside air temperature. There is no need to worry about freezing and deterioration.

【0033】図5の透水性不織布袋2は、円外周部に紐
2aが通されており、この紐を絞る事によって袋状にな
り、紐による絞りを暖め、開放してやる事によって円形
のシート状となるため、上記天日乾燥時には凝固物がシ
ート上にて乾燥が促進される事となる。又、このような
袋を用いる事によって、処理物の各移動時には容易な移
動を可能とする。
In the bag 2 shown in FIG. 5, a string 2a is passed through the outer periphery of the circle, and the string is squeezed to form a bag. The squeezing by the string is heated, and the bag is opened to form a circular sheet. Therefore, the drying of the coagulated material on the sheet is promoted during the solar drying. In addition, by using such a bag, it is possible to easily move the processed material at each time.

【0034】凝固に供する薬剤は、予め二価鉄を中心と
しイオン化傾向の大きい金属類が混入した硅酸ソーダ3
号の規定希釈水溶液と鉱酸の10%以下の水溶液を適量
用意しておき、実施時には容器に印を付けた薬剤計量容
器4に、これらの水溶液を投入、計量し、添加する。
The agent to be used for coagulation is sodium silicate 3 previously mixed with metals having a high ionization tendency, mainly ferrous iron.
Appropriate amounts of a prescribed diluted aqueous solution of the above and an aqueous solution of 10% or less of mineral acid are prepared, and these aqueous solutions are charged, measured, and added to the medicine measuring container 4 marked on the container at the time of execution.

【0035】泥状物をタンク等に直接投入する場合は、
図7に示されるタンク1aに泥状物3を投入する。この
タンクは地盤を掘り下げた掘削ポンドや鋼製の箱形形式
槽でもミキサー等でもよい。図7は箱形形式槽1aに泥
状物3を投入した状態図である。
When the mud is directly charged into a tank or the like,
The muddy substance 3 is put into the tank 1a shown in FIG. This tank may be an excavated pond or a box-type tank made of steel or a mixer. FIG. 7 is a diagram showing a state in which the muddy substance 3 is put into the box-shaped tank 1a.

【0036】図8は、硅酸ソーダ3号を希釈水によって
40〜50%の希釈硅酸ソーダ水溶液4aを製造、薬剤
計量容器4に貯留、泥状物3に希釈硅酸ソーダ水溶液4
aを投入、撹拌混合される。次に、調整され薬剤計量容
器4に貯留された活性硅酸ゾル4bを投入し、全体によ
く撹拌混合する。撹拌混合が完了した後、10〜40分
間程度静かに放置すると、ゲル状含水凝固物が生成され
る。撹拌混合は、極力上下に撹拌混合することが要求さ
れる。
FIG. 8 shows that a sodium silicate No. 3 is prepared with a diluted water to prepare a 40-50% diluted sodium silicate aqueous solution 4a, stored in a chemical measuring container 4, and a mud 3 is diluted with a diluted sodium silicate aqueous solution 4.
a, and mixed by stirring. Next, the activated silicic acid sol 4b adjusted and stored in the medicine measuring container 4 is charged, and the whole is thoroughly stirred and mixed. After the stirring and mixing are completed, the mixture is left gently for about 10 to 40 minutes to produce a gel-like hydrated coagulated product. The stirring and mixing are required to be mixed up and down as much as possible.

【0037】この様に生成された含水凝固物6は、タン
ク1aより取り出し、図9の如く地面上に所定の厚みに
盛り上げ、天日乾燥により、大きく減容された物理的、
化学的に安定した中性の砂質系土砂に類似する硬質団粒
8を短期日に生成せしめ得る。この場合、含水凝固物6
を所定の厚みに盛り上げることにより、その下部部分は
上部凝固物の自重を外力とした静圧脱水が行われ、一時
的に相当量の水分を急激に排出することとなり、乾燥を
促進助長する効果をもつ。図10に、この様な水分の排
出過程を説明する。
The hydrated coagulated product 6 thus generated is taken out of the tank 1a, and is raised to a predetermined thickness on the ground as shown in FIG.
Hard aggregates 8 similar to chemically stable neutral sandy sediment can be produced on short days. In this case, the hydrated coagulate 6
The lower part is subjected to static pressure dehydration using the own weight of the upper coagulated material as an external force, and a considerable amount of water is temporarily suddenly discharged, thereby promoting drying. With. FIG. 10 illustrates such a process of discharging water.

【0038】[0038]

【発明の効果】本発明は、以上、説明したように、泥状
物の簡易凝固減容安定化工法として、次のような効果を
供えている。
As described above, the present invention provides the following effects as a simple solidification volume reduction stabilization method for mud.

【0039】泥状物を熟練度を要さない簡単な作業で、
比較的短期日に泥状物容量を減容、安定化して、かつ、
残さの取扱いを容易とする。更に、泥状物の物性に関わ
らず、減容安定化処理を容易に可能とし、一部用具、又
は簡単な機器を除けば特殊な機械設備を用いる事なく、
容易に泥状物の減容安定化ができる。
[0039] The muddy material is a simple operation that does not require skill,
Reduce and stabilize mud volume on relatively short days, and
Easy handling of residue. Furthermore, regardless of the physical properties of the mud, the volume reduction stabilization process can be easily performed without using special equipment except for some tools or simple equipment.
The volume of mud can be easily reduced and stabilized.

【0040】透水性不織布袋を用いる事によって、各作
業工程間の移動が非常にスムーズに行われる。更に、こ
の透水性不織布袋は透水性に優れているため、一時的に
有効な脱水効果をも合わせ持っている。
By using the water-permeable nonwoven bag, the movement between the respective working steps can be performed very smoothly. Furthermore, since this water-permeable nonwoven bag is excellent in water permeability, it also has a temporarily effective dewatering effect.

【0041】活性硅酸ゾルと希釈硅酸ソーダによって、
泥状物を中性のゲル状含水凝固物とした後に、脱水処理
や天日乾燥により減容化するようにしているために、減
容化工程での分離水も減容安定化された硬質団粒も無害
であり、環境に悪い影響を与える事がない。更に、この
凝固物は物理的、化学的に長期安定しているため、天日
乾燥に対しても凍結や降雨等による凝固物の流出や再度
の泥状化の恐れがないために、非常に短期日で大きく減
容され、安定化した硬質団粒を得ることが出来ると供
に、作業日程も把握できる。しかも、得られた硬質団粒
を有効に利用する事もできる。
With the activated silicate sol and the diluted sodium silicate,
After the mud is turned into a neutral gel-like hydrated coagulate, the volume is reduced by dehydration and drying in the sun. Aggregates are also harmless and do not adversely affect the environment. Furthermore, since the coagulated material is physically and chemically stable for a long period of time, there is no danger of the coagulated material flowing out due to freezing or rainfall and re-mudification even in solar drying. In addition to being able to obtain stabilized hard aggregates with a large volume reduction in a short period of time, the work schedule can be grasped. Moreover, the obtained hard aggregates can be effectively used.

【0042】実験。昭和48年環境庁告示第13号、昭
和57年環境庁告示第44号に基づき、含水凝固物、生
成硬質団粒、分離水の有害物質溶出試験を行った。試験
結果は、満足する結果を得た。
Experiment. Based on Notification No. 13 of the Environment Agency in 1973 and No. 44 Notification of the Environment Agency in 1982, leaching tests of hydrated coagulates, formed hard aggregates, and separated water were conducted. The test results were satisfactory.

【0043】泥状物の凝固減容安定化に対する1全作業
工程は4〜14日を要するが、その間の実作業稼働時間
は1〜2時間を要するのみで、かつ、熱や大掛かりな機
械、特殊な機械を使用しないために、エネルギーの消費
が少なく、一層の経済性をもたらす事となる。
One entire working process for the stabilization of the solidification and volume reduction of the mud requires 4 to 14 days, but the actual working time in the meantime requires only 1 to 2 hours, and heat and large-scale machines, Since no special machine is used, energy consumption is low, which leads to further economic efficiency.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の泥状物凝固実施の1例を概略的に示す
泥状物凝固前の断面図である。
FIG. 1 is a cross-sectional view schematically showing an example of the implementation of the muddy solidification of the present invention before muddy solidification.

【図2】薬剤添加、撹拌混合の概略図である。FIG. 2 is a schematic diagram of addition of a drug and stirring and mixing.

【図3】含水凝固物の吊り下げ一次脱水の概略図であ
る。
FIG. 3 is a schematic diagram of hanging primary dehydration of a hydrated coagulated product.

【図4】一次脱水後の天日乾燥の概略図である。FIG. 4 is a schematic diagram of solar drying after primary dehydration.

【図5】透水性不織布袋の概略平面図と透水性不織布の
構成図である。
FIG. 5 is a schematic plan view of a water-permeable nonwoven fabric bag and a configuration diagram of a water-permeable nonwoven fabric.

【図6】含水凝固物の透水性不織布袋による吊り下げ一
次脱水作用の説明図である。
FIG. 6 is an explanatory view of a primary dehydration action of a water-containing coagulated product suspended by a water-permeable nonwoven bag.

【図7】本発明の泥状物凝固実施の2例を概略的に示す
タンクに泥状物を投入した凝固前の状態図である。
FIG. 7 is a state diagram before solidification in which mud is put into a tank, schematically showing two examples of execution of mud solidification according to the present invention.

【図8】薬剤添加、撹拌混合の概略図である。FIG. 8 is a schematic diagram of drug addition and stirring and mixing.

【図9】所定の厚みに盛土、天日乾燥の概略図である。FIG. 9 is a schematic view of embankment to a predetermined thickness and solar drying.

【図10】含水凝固物の天日乾燥による含有水分の排出
過程説明図である。
FIG. 10 is an explanatory diagram of a process of discharging water content by drying a water-containing coagulated product by sunlight.

【符号の説明】[Explanation of symbols]

1 上部開放形タンク 1a タンク 2 透水性不織布袋 2a 透水性不織布袋とじ紐 3 泥状物 4 薬剤計量容器 4a 希釈硅酸ソーダ水溶液 4b 活性硅酸ゾル 5 撹拌混合棒 6 含水凝固物 7 一次脱水用吊り下げ柱 8 生成硬質団粒 DESCRIPTION OF SYMBOLS 1 Top-open tank 1a Tank 2 Water-permeable nonwoven bag 2a Water-permeable nonwoven bag binding cord 3 Mud 4 Drug measuring container 4a Dilute sodium silicate aqueous solution 4b Active silica sol 5 Stirring and mixing rod 6 Water-containing coagulated material 7 Primary dehydration Suspended pillar 8 Generated hard aggregate

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 浚渫汚泥やヘドロ、各種廃水スラッジ等
の親水性泥状物を、バケツまたは上部開放形タンク等の
内側に設置された上部が開放された透水性のよい袋に投
入するか、バケツまたは上部開放形タンク等に直接投入
し、二価鉄を中心としたイオン化傾向の大きい金属類を
混入させた硅酸物質水溶液と鉱酸とを混合して得られた
酸性の活性硅酸ゾルとアルカリ性の希釈硅酸物質水溶液
を添加して撹拌混合し、この親水性泥状物を中性の含水
凝固物とする工程と、 この含水凝固物を袋に入れたまま取り出し、一時的に吊
り下げる事によるか、または、この含水凝固物を直接取
り出し、所定の層厚に積み上げる事により、含水凝固物
静重量を利用した強制的一次脱水を行い、その後、袋を
用いた場合は、この袋上部を全開放状態として地面上ま
たは架台上に放置し、袋を用いない場合は、継続放置す
る事により、凝固反応作用による縮合反応に伴う含水凝
固物よりの離漿反応と天日乾燥工程による二次脱水作用
にて短期日で、減容された物理的、化学的に安定した中
性域での再泥化しない砂質系土砂に類似する硬質団粒を
生成せしめる工程とを、包含する泥状物の簡易凝固減容
安定化工法。
Claims 1. A hydrophilic mud such as dredged sludge, sludge, and various kinds of wastewater sludge is put into a bucket or a bag having good open permeability installed inside a tank or an open top tank, An acidic activated silicate sol obtained by directly charging a bucket or open-top tank, etc., and mixing an aqueous solution of a silicate substance mixed with highly ionizable metals such as ferrous iron and a mineral acid. And a process of adding an alkaline dilute silicate aqueous solution and mixing with stirring to make this hydrophilic muddy substance into a neutral hydrated coagulated product, and taking out the hydrated coagulated product in a bag and temporarily suspending it. By lowering, or by directly taking out the hydrated coagulated material and stacking it to a predetermined layer thickness, forcible primary dehydration using the hydrated coagulated material static weight is performed. The top is fully open and the ground Alternatively, if the bag is not used and the bag is left on the gantry, it can be left standing for a short period of time due to the syneresis reaction from the hydrated coagulated product due to the condensation reaction due to the coagulation reaction and the secondary dehydration by the solar drying process. Producing hard aggregates similar to sandy soil that does not re-pulverize in a neutral region where the volume is reduced physically and chemically stable, Stabilization method.
JP2000161198A 2000-04-21 2000-04-21 Method for simply coagulating muddy material decreasing volume thereof and stabilizing the same Pending JP2001300591A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000161198A JP2001300591A (en) 2000-04-21 2000-04-21 Method for simply coagulating muddy material decreasing volume thereof and stabilizing the same

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000161198A JP2001300591A (en) 2000-04-21 2000-04-21 Method for simply coagulating muddy material decreasing volume thereof and stabilizing the same

Publications (1)

Publication Number Publication Date
JP2001300591A true JP2001300591A (en) 2001-10-30

Family

ID=18665261

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000161198A Pending JP2001300591A (en) 2000-04-21 2000-04-21 Method for simply coagulating muddy material decreasing volume thereof and stabilizing the same

Country Status (1)

Country Link
JP (1) JP2001300591A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004008937A (en) * 2002-06-07 2004-01-15 Sumitomo Forestry Co Ltd Method and bag for purifying cement washing water
CN117645455A (en) * 2024-01-30 2024-03-05 天津中岩大地材料科技有限公司 Dredged silt curing material and pipeline curing hydraulic filling method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004008937A (en) * 2002-06-07 2004-01-15 Sumitomo Forestry Co Ltd Method and bag for purifying cement washing water
CN117645455A (en) * 2024-01-30 2024-03-05 天津中岩大地材料科技有限公司 Dredged silt curing material and pipeline curing hydraulic filling method
CN117645455B (en) * 2024-01-30 2024-03-26 天津中岩大地材料科技有限公司 Dredged silt curing material and pipeline curing hydraulic filling method

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