JP2003154370A - Method for water treatment/sludge treatment without using chemical - Google Patents

Method for water treatment/sludge treatment without using chemical

Info

Publication number
JP2003154370A
JP2003154370A JP2001316463A JP2001316463A JP2003154370A JP 2003154370 A JP2003154370 A JP 2003154370A JP 2001316463 A JP2001316463 A JP 2001316463A JP 2001316463 A JP2001316463 A JP 2001316463A JP 2003154370 A JP2003154370 A JP 2003154370A
Authority
JP
Japan
Prior art keywords
water
treated
cake
powdery substance
clay
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
JP2001316463A
Other languages
Japanese (ja)
Inventor
Tadayoshi Nagaoka
忠義 永岡
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP2001316463A priority Critical patent/JP2003154370A/en
Publication of JP2003154370A publication Critical patent/JP2003154370A/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

Landscapes

  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Treatment Of Sludge (AREA)
  • Filtration Of Liquid (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method for water treatment/sludge treatment which can precipitate suspended solids in raw water without using a flocculant and treat sludge efficiently. SOLUTION: At least one of red clay and clay after being dried is pulverized into powder, the powder is added into the raw water containing the suspended solids, and the mixture after being agitated is allowed to stand for a prescribed time, so that the suspended solids are precipitated together with the powder, and the supernatant is taken out. The used powder can be reused after being dried again. The raw water containing the suspended solids or raw sludge is added with the powder, and the mixture is treated after being agitated by a solid-liquid separator to be separated into cake and filtrate. The filtrate is separated into precipitate and supernatant, and the supernatant is taken out.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は凝集剤等の薬品を使
用しないで多量の浮遊物資を含有する被処理水から浮遊
物質を取り除くことができる水処理方法および被処理汚
泥に薬品を添加しないで効率的に処理することができる
汚泥処理方法に関する。
TECHNICAL FIELD The present invention relates to a water treatment method capable of removing suspended solids from treated water containing a large amount of suspended solids without using a chemical such as a flocculant, and adding no chemical to the treated sludge. The present invention relates to a sludge treatment method capable of treating efficiently.

【0002】[0002]

【従来の技術】従来浮遊物質(懸濁物質)を多量に含有
する水を処理する場合は、被処理水にPACや高分子凝
集剤等の凝集剤を添加し攪拌した後沈殿池に送り、オー
バーフロー水を一定の排出基準に基づいて排出する。ま
た処理水として利用する場合はオーバーフロー水を砂濾
過により急速濾過する場合もある。
2. Description of the Related Art Conventionally, when treating water containing a large amount of suspended matter (suspended matter), a coagulant such as PAC or a polymer coagulant is added to the water to be treated and the mixture is stirred and then sent to a sedimentation tank. Discharge overflow water based on certain emission standards. When used as treated water, overflow water may be rapidly filtered by sand filtration.

【0003】沈殿汚泥は系外に排出されて処理される。
往年は沈殿汚泥は天日乾燥により乾燥処理されていた
が、現在では一般に吸引式または加圧式の固液分離装置
からなる脱水式汚泥処理装置によりケーキと濾液に分離
する方法により処理している。脱水式汚泥処理装置とし
ては、真空吸引式のドラム型(濾布またはスクリーン方
式)または加圧式の濾布方式のフイルタープレス、ベル
トプレス、スクリーン使用によるスクリーンプレス等の
装置が代表的なものである。
The settled sludge is discharged to the outside of the system for treatment.
In the past, the settled sludge was dried by sun drying, but nowadays it is generally treated by a method of separating it into a cake and a filtrate by a dehydration type sludge treatment device consisting of a suction type or pressure type solid-liquid separation device. A typical example of the dehydration sludge treatment device is a vacuum suction drum type (filter cloth or screen type) or pressure type filter cloth type filter press, belt press, screen press using a screen, and the like. .

【0004】これらの脱水式汚泥処理装置においては、
汚泥処理を効率的に行なうために処理前の沈殿汚泥に再
び凝集剤を添加するのが普通である。
In these dehydration-type sludge treatment devices,
In order to efficiently carry out sludge treatment, it is usual to add a flocculant again to the settled sludge before treatment.

【0005】[0005]

【発明が解決しようとする課題】従来の水処理、汚泥処
理方法においては、被処理水中の浮遊物質を凝集沈殿さ
せるため、または汚泥処理を効率的に行なうために凝集
剤を添加する方法が使用されているが、この方法は凝集
剤の費用がかかるのみならず、処理水や汚泥処理後に残
る脱水ケーキには薬品が残り環境保護上問題が生じる場
合がある。環境保護のために薬品を処理水から除去する
には処理水をさらに薬品除去工程にかけねばならず、多
大の費用がかかる。また所定量以上の薬品が含有されて
いる脱水ケーキは法規上産業廃棄物扱いに指定されてい
るので、汚泥処理費用が嵩むという問題を生じる。
In the conventional water treatment and sludge treatment methods, a method of adding a flocculant is used in order to coagulate and settle suspended solids in water to be treated or to efficiently perform sludge treatment. However, this method not only costs the cost of the flocculant, but also chemicals remain in the treated water and the dehydrated cake remaining after sludge treatment, which may cause environmental problems. In order to remove the chemicals from the treated water for the purpose of environmental protection, the treated water has to be further subjected to the chemical removal process, which is very expensive. In addition, since dehydrated cakes containing a predetermined amount or more of chemicals are designated as industrial wastes by law, there arises a problem that sludge treatment costs increase.

【0006】本発明は、被処理水中の浮遊物質を凝集沈
殿させるためまたは汚泥処理を効率的に行なうために凝
集剤を使用する従来の方法の問題点にかんがみなされた
ものであって、凝集剤を使用することなく被処理水中の
浮遊物質を沈殿させることができまた汚泥処理を効率的
に行なうことができる環境に配慮した新規な水処理・汚
泥処理方法を提供しようとするものである。
The present invention has been made in view of the problems of the conventional method of using a coagulant for coagulating sedimentation of suspended solids in water to be treated or for efficiently treating sludge. It is intended to provide a new environmentally friendly water treatment / sludge treatment method capable of precipitating suspended solids in water to be treated without the use of water and efficiently performing sludge treatment.

【0007】[0007]

【課題を解決する手段および作用】上記課題を解決する
ため、本発明者は鋭意研究と実験を重ねた結果、赤土お
よび粘土の少なくとも1種を乾燥した後粉砕して粉状物
質とし、浮遊物質を含有する被処理水に該粉状物質を添
加して攪拌した後所定時間静置すると、意外なことに浮
遊物質は該粉状物質とともに沈降して沈殿物と上澄み水
に分離することを発見し、本発明に到達した。
Means and Actions for Solving the Problems To solve the above problems, the present inventor has conducted extensive studies and experiments, and as a result, at least one of red clay and clay was dried and then pulverized into a powdery substance, It was discovered that, when the powdery substance is added to water to be treated containing water, and the mixture is left to stand for a predetermined time after being stirred, the floating substance sediments together with the powdery substance and separates into a precipitate and supernatant water. Then, the present invention has been reached.

【0008】すなわち、上記目的を達成する本発明の薬
品を使用しない水処理方法は、赤土および粘土の少なく
とも1種を乾燥した後粉砕して粉状物質とし、浮遊物質
を含有する被処理水に該粉状物質を添加して攪拌した後
所定時間静置することにより浮遊物質を該粉状物質とと
もに沈降させ、次いで後上澄み水を取出すことを特徴と
するものである。
That is, the chemical-free water treatment method of the present invention which achieves the above-mentioned object is to dry at least one of red clay and clay and then pulverize it into a powdery substance to prepare water to be treated containing suspended substances. The present invention is characterized in that the powdery substance is added and stirred and then left standing for a predetermined time to precipitate the floating substance together with the powdery substance, and then the supernatant water is taken out.

【0009】本発明によれば、上記粉状物質は被処理水
中の浮遊物質を凝集沈降させる凝集剤としての作用を有
し、浮遊物質を濾過槽の濾過層(砂層)上または容器の
底面上に沈殿させ、被処理水を上澄み水と沈殿物に分離
する。したがって、上澄み水のみを系外に取出すことに
よって、上澄み水は薬品処理のためのさらなる処理にか
ける必要がなく、また濾過槽または容器に残存する沈殿
物は、薬品を含まない赤土または粘土であるから産業廃
棄物としての扱いを受けることなく容易に処理すること
ができる。
According to the present invention, the powdery substance has a function as a flocculant for flocculating and suspending the suspended substance in the water to be treated, and the suspended substance is on the filter layer (sand layer) of the filter tank or on the bottom surface of the container. The treated water is separated into supernatant water and a precipitate. Therefore, by removing only the supernatant water from the system, the supernatant water does not need to be further processed for chemical treatment, and the precipitate remaining in the filter tank or container is chemical-free red clay or clay. Can be easily treated without being treated as industrial waste.

【0010】上記方法により沈降した粉状物質は、これ
を取出して再度乾燥した後粉砕して粉状物質として被処
理水中の浮遊物質沈殿に再利用することができる。
The powdery substance precipitated by the above method can be taken out, dried again, and then pulverized to be reused as a powdery substance for precipitation of suspended solids in the water to be treated.

【0011】本発明の1側面においては、浮遊物資を含
有する被処理水に赤土を添加して攪拌した後所定時間静
置することにより浮遊物質を赤土とともに沈降させ、次
いで上澄み水を取出すことを特徴とする。
In one aspect of the present invention, red soil is added to water to be treated containing suspended solids, and the mixture is stirred and allowed to stand for a predetermined time so that the suspended solids are allowed to settle with the red soil, and then the supernatant water is removed. Characterize.

【0012】本発明の1側面においては、薬品を使用し
ない水処理方法は、赤土および粘土の少なくとも1種を
乾燥した後粉砕して粉状物質とし、浮遊物質を含有する
被処理水に該粉状物質を添加して攪拌混合した後この混
合物を固液分離装置により処理してケーキと濾液に分離
させ、該濾液を沈殿物と上澄み水に分離させた後該上澄
み水を取出すことを特徴とする。
In one aspect of the present invention, a chemical-free water treatment method is a method in which at least one of red clay and clay is dried and then pulverized into a powdery substance, which is added to water to be treated containing suspended matter. After adding substances like substances and stirring and mixing, the mixture is treated with a solid-liquid separator to separate into a cake and a filtrate, and the filtrate is separated into a precipitate and supernatant water, and then the supernatant water is taken out. To do.

【0013】この上澄み水は凝集剤を含んでいないので
薬品除去のためのさらなる処理にかける必要がなく、ま
たケーキおよび濾液の沈殿物も凝集剤を含んでいないの
で、産業廃棄物としての扱いを受けることなく容易に処
理することができる。
Since this supernatant water does not contain a coagulant, it does not need to be further processed for chemical removal, and the cake and filtrate precipitates do not contain a coagulant, so that it should be treated as industrial waste. It can be easily processed without receiving.

【0014】本発明の1側面においては、この方法によ
り生成したケーキおよび濾液沈殿物を取出して乾燥させ
た後粉砕して粉状物質とし、被処理水に添加して再利用
することができる。
In one aspect of the present invention, the cake and filtrate precipitate produced by this method can be taken out, dried and then pulverized into a powdery substance, which can be added to the water to be treated and reused.

【0015】本発明の1側面においては、赤土および粘
土の少なくとも1種を乾燥した後粉砕して粉状物質と
し、被処理汚泥に該粉状物質を添加して攪拌混合した後
この混合物を固液分離装置により処理してケーキと濾液
に分離させ、該濾液を沈殿物と上澄み水に分離させた後
該上澄み水を取出すことを特徴とする、薬品を使用しな
い汚泥処理方法が提供される。
In one aspect of the present invention, at least one of red clay and clay is dried and then pulverized into a powdery substance, the powdery substance is added to the sludge to be treated, and the mixture is stirred and mixed. There is provided a sludge treatment method using no chemicals, which comprises treating with a liquid separation device to separate a cake and a filtrate, separating the filtrate into a precipitate and supernatant water, and then removing the supernatant water.

【0016】粉状物質を凝集剤として使用することによ
り他の凝集剤を使用しないでも有効に良好なケーキ(含
水率が適度なケーキ)を形成することができ、効率良く
汚泥処理を達成することができる上に、形成されたケー
キは薬品を含有していないので、産業廃棄物としての扱
いを受けず容易に廃棄処理することができる。
By using a powdery substance as a coagulant, it is possible to effectively form a good cake (cake having an appropriate water content) without using any other coagulant, and to achieve efficient sludge treatment. In addition, since the formed cake does not contain chemicals, it can be easily disposed of without being treated as industrial waste.

【0017】本発明の1側面においては、この汚泥処理
方法により生成したケーキおよび濾液沈殿物を取出して
乾燥させた後粉砕して粉状物質とし、被処理汚泥に添加
して再利用することができる。
In one aspect of the present invention, the cake and filtrate precipitate produced by this sludge treatment method can be taken out, dried and then pulverized into a powdery substance, which can be added to the sludge to be reused. it can.

【0018】本発明の1側面においては、薬品を使用し
ない水処理方法は、赤土、粘土および炭化物の少なくと
も1種を乾燥した後粉砕して粉状物質とし、この粉状物
質を水に溶いて水溶液を調製し、この水溶液中に水没さ
せた円筒形スクリーンドラムの内側から真空吸引を行う
ことによりスクリーンドラムの外周に該粉状物質から成
るフイルター層を予め形成し、このフイルター層が外周
に形成されたスクリーンドラムを被処理水中に水没また
は半水没させた状態で該スクリーンドラムの該フイルタ
ー層の内側から真空吸引を行うことにより被処理水の濾
過を行うことを特徴とする。
In one aspect of the present invention, a chemical-free water treatment method is a method in which at least one of red clay, clay and carbide is dried and then pulverized into a powdery substance, and the powdery substance is dissolved in water. An aqueous solution is prepared, and a vacuum suction is performed from the inside of the cylindrical screen drum submerged in the aqueous solution to form a filter layer made of the powdery substance on the outer circumference of the screen drum in advance, and this filter layer is formed on the outer circumference. The treated water is filtered by performing vacuum suction from the inside of the filter layer of the screen drum in a state where the screen drum is submerged or semi-submerged in the treated water.

【0019】この方法においても、粉状物質を凝集剤と
するフイルター層を形成することにより、他の凝集剤を
使用しないでも円筒状スクリーンのフイルター層の外周
に有効に良好なケーキを形成することができ、水処理を
効率良く行うことができる上に、形成されたケーキは産
業廃棄物としての取扱を受けずに容易に廃棄処理するこ
とができる。
Also in this method, by forming a filter layer using a powdery substance as a coagulant, it is possible to effectively form a good cake on the outer periphery of the filter layer of the cylindrical screen without using another coagulant. In addition to being able to efficiently perform water treatment, the formed cake can be easily disposed of without being treated as industrial waste.

【0020】スクリーンドラムを回転させながらこの方
法により被処理水の濾過を行い、該スクリーンドラムの
該フイルター層の外周に形成された濾滓ケーキ層をスク
レーパーにより掻き落として連続濾過を行うこともでき
る。
It is also possible to carry out continuous filtration by filtering the water to be treated by this method while rotating the screen drum, and scraping off the filter cake layer formed on the outer periphery of the filter layer of the screen drum with a scraper. .

【0021】また、この方法により掻き落とした濾滓ケ
ーキを固液分離装置により処理してケーキと濾液に分離
させ、該濾液を沈殿物と上澄み水に分離させた後該上澄
み水を取出すこともできる。スクリーンドラムが半水没
状態で濾過を行う場合は掻き落とされる濾滓ケーキは脱
水ケーキとなっているので固液分離する必要はない。
It is also possible to treat the cake of cake scraped off by this method with a solid-liquid separator to separate it into a cake and a filtrate, separate the filtrate into a precipitate and supernatant water, and then take out the supernatant water. it can. When filtration is performed with the screen drum submerged in water, the cake cake scraped off is a dehydrated cake, and therefore solid-liquid separation is not necessary.

【0022】また、この方法により取出されたケーキお
よび沈殿物または脱水ケーキを再度乾燥した後粉砕して
粉状物資として再利用することもできる。
Further, the cake and the precipitate or the dehydrated cake taken out by this method can be dried again and then pulverized to be reused as a powdery material.

【0023】[0023]

【発明の実施の態様】以下本発明の実施の態様について
説明する。本明細書において、「粘土」とは粘土鉱物を
主体とする岩石、土壌で適量の水を混ぜてこねると可塑
性を有し、乾けば剛性を示し、高い温度で焼けば焼結す
るものを意味し、「赤土」とは鉄分を含み、赤く黄ばん
だ粘土を意味し、赤黄色土、暗赤色土および赤玉土を含
む。実験の結果、赤土の中で特に沖縄県の国領(くにが
み)マージと呼ばれる赤土が凝集効果が大きく有効であ
ることが判った。国領マージは沖縄本島北部・久米島東
部・石垣島・西表島などの山地、丘陵の多い島に分布す
る赤土で、砂岩、泥岩、火成岩、変成岩などの基盤岩類
の風化土壌である。赤土としては他の多くの種類の赤土
が本発明の目的達成のために使用可能である。また粘土
としては、信楽白土などの陶土、磁器土など多くの種類
の粘土が使用可能である。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described below. In the present specification, the term "clay" means a rock mainly composed of clay minerals, which has plasticity when kneaded with an appropriate amount of water in soil, exhibits plasticity when dried, and sinters when burned at a high temperature. However, "red soil" means iron-containing, reddish-yellow clay, and includes red-yellow soil, dark-red soil, and red-ball soil. As a result of the experiment, it was found that among the red soil, the red soil called "Kunigami merge" in Okinawa Prefecture has a large agglomeration effect and is effective. The Kokuryo Merge is a red soil distributed in mountains such as the northern part of Okinawa main island, eastern Kume Island, Ishigaki Island, Iriomote Island, etc. As the red soil, many other types of red soil can be used for the purpose of the present invention. As clay, many kinds of clay such as Shigaraki clay and porcelain clay can be used.

【0024】本発明において使用する赤土または粘土の
粉状物質を作成するには、赤土または粘土を熱風式乾燥
機等によりまたは天日乾燥により充分に乾燥させた後粉
砕機等により粉状になるまで粉砕する。粉状物質の各粒
の粒径は特に限定はないが、粒径はなるべく小さい方が
有効であり、0.005mm以下が好ましい。
In order to prepare a powdery substance of red soil or clay used in the present invention, the red soil or clay is sufficiently dried by a hot air dryer or the like, or is dried by sun drying, and then powdered by a pulverizer or the like. Crush up to. The particle size of each particle of the powdery substance is not particularly limited, but it is effective that the particle size is as small as possible, and 0.005 mm or less is preferable.

【0025】被処理水を濾過槽または容器において処理
することにより浮遊物質を粉状物質とともに濾過槽の濾
過層または容器の底面に沈降させる場合は、粉状物質を
被処理水に所定量添加後充分に攪拌混合した後所定時間
静置する。粉状物質の添加量および静置時間は被処理水
の性質および粉状物質の種類、処理の目的等により異な
る。一般的には粉状物質の添加量が多いほど浮遊物質の
凝集沈殿速度は速く、静置時間が長いほど浮遊物質の沈
殿率は大きい。
In the case where suspended solids are settled together with powdery substances on the filtration layer of the filtration tank or the bottom surface of the container by treating the water to be treated in the filtration tank or container, after adding a predetermined amount of the powdery substances to the water to be treated. After sufficiently stirring and mixing, leave still for a predetermined time. The amount of powdery substance added and the standing time vary depending on the nature of the water to be treated, the type of powdery substance, the purpose of treatment, and the like. Generally, the larger the amount of the powdery substance added, the faster the rate of flocculation and settling of floating substances, and the longer the standing time, the greater the rate of precipitation of floating substances.

【0026】浮遊物質が実質的に沈降した上澄み水を系
外に取出した後に残る浮遊物質が表面に付着した粉状物
質は、これを取り出し、加熱乾燥させることによって、
表面に付着した浮遊物質は大半が焼失しあるいは飛散
し、乾燥した粉状物質を再度粉砕することにより、次の
水処理工程において添加する粉状物質として再利用する
ことができる。この場合、粉状物質はすでに最初の粉砕
工程において微細な粉状に粉砕されているので、再利用
の際は、粉状物質はたとえば粒径5mm〜10mm程度
の比較的に大きい粒ないし塊であっても被処理水に添
加、攪拌することにより凝集効果を発揮することができ
る。
The powdery substance having the floating substance remaining on the surface thereof after the supernatant water in which the floating substance has substantially settled is taken out of the system is taken out and dried by heating.
Most of the floating substances adhering to the surface are burnt out or scattered, and the dried powdery substance can be reused as a powdery substance added in the next water treatment step by pulverizing again. In this case, since the powdery substance has already been pulverized into a fine powder in the first crushing step, the powdery substance is, for reuse, formed into relatively large particles or lumps having a particle size of, for example, 5 mm to 10 mm. Even if it is present, the aggregation effect can be exhibited by adding it to the water to be treated and stirring it.

【0027】粉状物質は赤土または粘土を単独で使用し
てもよいし、両者を適当な比率で混合して使用してもよ
い。両者を混合する場合、混合比率は粉状物質としての
使用の目的に応じて適当な値に設定すればよい。
As the powdery substance, red clay or clay may be used alone, or both may be mixed and used at an appropriate ratio. When both are mixed, the mixing ratio may be set to an appropriate value depending on the purpose of use as a powdery substance.

【0028】赤土の中で国領マージのように容易に水に
溶けて分解する性質のものは、乾燥し粉砕する工程を経
ずに採取した赤土を直接被処理水に添加し、攪拌するこ
とによってある程度浮遊物質の凝集沈殿効果を奏するこ
とが判った。ただ充分な効果を挙げるには赤土を乾燥し
粉砕して粉状物質として添加することが望ましい。赤土
の中でも容易に水に溶けない性質のものおよびその他の
粘土は乾燥、粉砕工程を経ずに採取したままの状態のも
のを直接被処理水に添加しても浮遊物質を凝集沈殿させ
る効果はほとんどない。
[0028] Among the red soil, the one that has the property of easily dissolving in water and decomposing like the national territory merge, by adding the red soil collected without the step of drying and crushing directly to the water to be treated and stirring it. It was found that a certain degree of flocculation and sedimentation effect of suspended solids was achieved. However, in order to obtain a sufficient effect, it is desirable to dry and grind the red clay and add it as a powdery substance. Even if red clay that does not readily dissolve in water and other clays are added directly to the water to be treated without drying and crushing, the effect of aggregating and suspending suspended solids is not rare.

【0029】粉状物質を被処理水に添加し、攪拌混合し
た後この混合物を固液分離装置により処理してケーキと
濾液に分離する水処理方法、すなわち粉状物質をケーキ
形成用の助剤として使用する方法においては、被処理水
に対する粉状物質の混合比は、被処理水中の浮遊物質を
粉状物質とともに沈降させる水処理方法の場合に比べて
はるかに大きくする必要がある。その混合比は、被処理
水の性質、粉状物質の種類、使用する固液分離装置の種
類等により異なる。一例として米国特許第5,618,
424号記載の固液分離装置と同型の固液分離装置を使
用した場合における混合比は1:1の場合に最適のケー
キが形成された。
A water treatment method in which a powdery substance is added to water to be treated, stirred and mixed, and then the mixture is treated by a solid-liquid separator to separate a cake and a filtrate, that is, an auxiliary agent for forming the powdery substance into a cake. In this method, the mixing ratio of the powdery substance to the water to be treated needs to be much higher than that in the case of the water treatment method in which the suspended solids in the water to be treated are settled together with the powdery substance. The mixing ratio varies depending on the nature of the water to be treated, the type of powdery substance, the type of solid-liquid separator used, and the like. As an example, US Pat. No. 5,618,
When the solid-liquid separator of the same type as the solid-liquid separator described in No. 424 was used, the optimum cake was formed when the mixing ratio was 1: 1.

【0030】この方法においても、固液分離装置により
ケーキと分離された濾液はなお多量の粉状物質を含んで
いるが、この濾液を静置すると、濾液は上澄み水と沈殿
物に急速に分離し、上澄み水を系外に取出すことができ
る。また、ケーキおよび濾液から上澄み水を取出した後
に残る沈殿物を再度乾燥し粉砕して粉状物質とすること
によりこの粉状物質を次の水処理工程において再利用す
ることができる。またこのケーキおよび沈殿物は薬品を
一切含んでいないので産業廃棄物として処理する必要は
なく、容易に廃棄することができる。
Also in this method, the filtrate separated from the cake by the solid-liquid separator still contains a large amount of powdery substances, but when this filtrate is allowed to stand, the filtrate is rapidly separated into supernatant water and a precipitate. However, the supernatant water can be taken out of the system. In addition, the precipitate remaining after removing the supernatant water from the cake and the filtrate can be reused in the next water treatment step by drying and pulverizing the precipitate again to give a powder. Further, since the cake and the precipitate do not contain any chemicals, they do not need to be treated as industrial waste and can be easily discarded.

【0031】上記粉状物質はは、ヘドロ等の一般汚泥を
固液分離装置にかけて脱水処理する場合にも凝集剤とし
て有効に使用することができる。その場合被処理汚泥と
粉状物質の混合率は使用目的によって異なるが、おおむ
ね1:1ないし1:2程度が好ましい。
The above powdery substance can be effectively used as a flocculant even when general sludge such as sludge is subjected to a dehydration treatment by applying it to a solid-liquid separator. In this case, the mixing ratio of the sludge to be treated and the powdery substance varies depending on the purpose of use, but it is preferably about 1: 1 to 1: 2.

【0032】本発明の1実施態様にかかる薬品を使用し
ない水処理方法は、赤土、粘土および炭化物の少なくと
も1種を乾燥した後粉砕して粉状物質とし、この粉状物
質を水に溶いて水溶液を調製し、この水溶液中に水没さ
せた円筒形スクリーンドラムの内側から真空吸引を行う
ことによりスクリーンドラムの外周に該粉状物質から成
るフイルター層を予め形成し、このフイルター層が外周
に形成されたスクリーンドラムを被処理水中に水没また
は半水没させた状態で該スクリーンドラムの該フイルタ
ー層の内側から真空吸引を行うことにより被処理水の濾
過を行う。
A chemical-free water treatment method according to one embodiment of the present invention is a method in which at least one of red clay, clay, and carbide is dried and then pulverized into a powdery substance, and the powdery substance is dissolved in water. An aqueous solution is prepared, and a vacuum suction is performed from the inside of the cylindrical screen drum submerged in the aqueous solution to form a filter layer made of the powdery substance on the outer circumference of the screen drum in advance, and this filter layer is formed on the outer circumference. The water to be treated is filtered by performing vacuum suction from the inside of the filter layer of the screen drum with the screen drum thus submerged in the water to be treated or submerged in water.

【0033】この実施態様において、赤土、粘土は上記
実施形態の各種赤土、粘土を使用することができる。ま
た、炭化物としては、木炭、やしがら活性炭等植物性の
炭化物等が好適である。赤土、粘土、炭化物はそのいず
れかを単独で使用してもよいし2種以上を混合して私用
しても良い。
In this embodiment, as the red soil and clay, the various red soil and clay of the above embodiment can be used. As the charcoal, charcoal, vegetable charcoal such as coconut charcoal activated carbon and the like are preferable. Any one of red clay, clay, and carbide may be used alone, or two or more kinds may be mixed and used for private use.

【0034】粉状物質を水に溶いた水溶液は、図1の模
式的断面図に示すように、容器1に収容し、この水溶液
2中に円筒状スクリーンドラム3を水没状態で設置す
る。円筒状スクリーンドラム3としてはたとえば(株)
ナガオカ製210型吸引式脱水機(米国特許第5,61
8,424号記載の装置と同型の装置)を使用すること
ができる。この円筒状スクリーンドラム3は回転駆動可
能な両端が閉じたウエッジワイヤスクリーンからなり、
その一端部は濾過水出口管4を介して図示しない真空吸
引装置に接続されており、この真空吸引装置を作動させ
ることにより円筒状スクリーン内部を減圧することがで
きる。
An aqueous solution in which a powdery substance is dissolved in water is housed in a container 1 and a cylindrical screen drum 3 is placed in the aqueous solution 2 in a submerged state, as shown in the schematic sectional view of FIG. Examples of the cylindrical screen drum 3 include:
Nagaoka 210-type suction dehydrator (US Pat. No. 5,61
A device of the same type as the device described in No. 8,424) can be used. This cylindrical screen drum 3 is composed of a wedge wire screen which can be rotationally driven and whose both ends are closed.
One end thereof is connected to a vacuum suction device (not shown) through the filtered water outlet pipe 4, and the inside of the cylindrical screen can be depressurized by operating this vacuum suction device.

【0035】図1の状態で真空吸引を行うことにより、
粉状物質の水溶液2の水分は濾過液出口管4から吸引排
出され、円筒状スクリーンドラム3のの外周には図2に
示すように粉状物質からなるフイルター層5が形成され
る。こうしてフイルター層5が形成されたら粉状物質の
水溶液2を容器1から取出し、予め粉状物質のフイルタ
ー層5が外周に形成された円筒状スクリーンドラム3の
準備が完了する。
By performing vacuum suction in the state of FIG.
The water content of the powdery substance aqueous solution 2 is sucked and discharged from the filtrate outlet pipe 4, and a filter layer 5 made of the powdery substance is formed on the outer periphery of the cylindrical screen drum 3 as shown in FIG. When the filter layer 5 is formed in this manner, the aqueous solution 2 of the powdery substance is taken out from the container 1, and the preparation of the cylindrical screen drum 3 on which the filter layer 5 of the powdery substance is previously formed on the outer periphery is completed.

【0036】この円筒状スクリーンドラム3を使用して
被処理水の濾過を行う場合は、容器1に被処理水を充填
し円筒状スクリーンドラム3が被処理水に水没した状態
で真空吸引を行い濾過水出口官4から濾過水を取出すよ
うにして濾過を行う。
When the water to be treated is filtered using this cylindrical screen drum 3, the container 1 is filled with the water to be treated, and vacuum suction is performed while the cylindrical screen drum 3 is submerged in the water to be treated. Filtration is performed so that filtered water is taken out from the filtered water outlet 4.

【0037】また、図3に示すように、被処理水入口6
から被処理水7を容器1内に注入し、真空吸引を行いな
がら水没状態の円筒状スククリーンドラム3を回転駆動
する。これによって濾過された水は濾過液出口管4から
取出され、フイルター層5の外周には被処理水中の固形
分がケーキ層8となって堆積する。このケーキ層8は円
筒状スクリーンドラム3のフイルター層5に近接して配
置されたスクレーパ9によって掻き落とされ容器外に排
出される。この操作によって被処理水の連続濾過ができ
る。
Further, as shown in FIG. 3, the treated water inlet 6
The water 7 to be treated is poured into the container 1, and the cylindrical scclean drum 3 in a submerged state is rotationally driven while performing vacuum suction. The water filtered by this is taken out from the filtrate outlet pipe 4, and the solid content in the water to be treated is accumulated as a cake layer 8 on the outer periphery of the filter layer 5. The cake layer 8 is scraped off by a scraper 9 arranged close to the filter layer 5 of the cylindrical screen drum 3 and discharged to the outside of the container. This operation allows continuous filtration of the water to be treated.

【0038】また、図4に示すように、被処理水入口6
から被処理水7を容器1内に注入し、真空吸引を行いな
がら半水没状態の円筒状スクリーンドラム3を駆動回転
することにより、濾過された水は濾過液出口官4から取
出され、フイルター層5の外周には被処理水中の固形分
がケーキ層8となって堆積する。このケーキ層8は円筒
状スクリーンドラム3のフイルター層5に近接して被処
理水7の上方に配置されたスクレーパ9によって掻き落
とされ容器外に排出される。この操作によって被処理水
の連続濾過ができる。
Further, as shown in FIG. 4, the treated water inlet 6
The treated water 7 is poured into the container 1 from the above, and the semi-submerged cylindrical screen drum 3 is driven to rotate while vacuum suction is performed, so that the filtered water is taken out from the filtrate outlet 4 and the filter layer On the outer circumference of 5, the solid content in the water to be treated is accumulated as a cake layer 8. The cake layer 8 is scraped off by a scraper 9 arranged above the water to be treated 7 in the vicinity of the filter layer 5 of the cylindrical screen drum 3 and discharged to the outside of the container. This operation allows continuous filtration of the water to be treated.

【0039】[0039]

【実施例】1.水処理における赤土・粘土の凝集剤とし
ての使用 (実施例1)沖縄県の国領マージから得た赤土濁水(浮
遊物質濃度20,000mg/L)を被処理水として使
用した。沖縄県の国領マージをオリオン機械株式会社製
の熱風式直火型乾燥機(ORIONJET HEATER HPS 310E)
(出力1時間当たり30,000キロカロリー)により
温度200°で2時間熱風乾燥した後ハンマーで叩いて
粉砕し、粒径0.005mm以下の粉状物質を形成し
た。この粉状物質10ccをビーカーに収容した被処理
水300ccに添加し、攪拌混合した後5時間静置し
た。被処理水は浮遊物質および粉状物質の沈殿物と上澄
み水に分離し、沈殿物はビーカー底部に沈殿した。この
上澄み水を透視度計で測定したところ透視度は82mm
であった。また上澄み水中の浮遊物質濃度を測定したと
ころ98mg/Lであった。上澄み水と沈殿物の比率は
9:1であった。
[Example] 1. Use of Red Soil / Clay as a Flocculant in Water Treatment (Example 1) Red soil turbid water (concentration of suspended solids 20,000 mg / L) obtained from the Kokuryo merger of Okinawa Prefecture was used as water to be treated. Orion Machinery Co., Ltd.'s hot air direct fire dryer (ORIONJET HEATER HPS 310E)
(Outputting 30,000 kcal / hour) was dried with hot air at a temperature of 200 ° for 2 hours and then crushed by hammering to form a powdery substance having a particle size of 0.005 mm or less. 10 cc of this powdery substance was added to 300 cc of water to be treated contained in a beaker, and the mixture was stirred and mixed, and then allowed to stand for 5 hours. The water to be treated was separated into precipitates of suspended solids and powdery substances and supernatant water, and the precipitates were deposited at the bottom of the beaker. When this clear water was measured with a fluorometer, the transparency was 82 mm.
Met. The concentration of suspended solids in the supernatant water was measured and found to be 98 mg / L. The ratio of supernatant water to precipitate was 9: 1.

【0040】(実施例2)粉状物質として滋賀県信楽町
産の陶土である信楽白土を実施例1の方法により乾燥、
粉砕したものを使用した以外は実施例1と同一条件で被
処理水を処理した。被処理水は浮遊物質および粉状物質
の沈殿物と上澄み水に分離し、沈殿物はビーカー底部に
沈殿した。この上澄み水を透視度計で測定したところ透
視度は56mmであった。また上澄み水中の浮遊物質濃
度を測定したところ155mg/Lであった。上澄み水
と沈殿物の比率は9:1であった。
(Example 2) Shigaraki clay, which is a pottery clay produced in Shigaraki Town, Shiga Prefecture, was dried as a powdery substance by the method of Example 1,
The water to be treated was treated under the same conditions as in Example 1 except that the pulverized product was used. The water to be treated was separated into precipitates of suspended solids and powdery substances and supernatant water, and the precipitates were deposited at the bottom of the beaker. When this supernatant water was measured with a fluorometer, the transparency was 56 mm. The concentration of suspended solids in the supernatant water was measured and found to be 155 mg / L. The ratio of supernatant water to precipitate was 9: 1.

【0041】(実施例3)粉状物質として滋賀県信楽町
産の陶土である信楽赤土を実施例1の方法により乾燥、
粉砕したものを使用した以外は実施例1と同一条件で被
処理水を処理した。被処理水は浮遊物質および粉状物質
の沈殿物と上澄み水に分離し、沈殿物はビーカー底部に
沈殿した。この上澄み水を透視度計で測定したところ透
視度は32mmであった。また上澄み水中の浮遊物質濃
度を測定したところ306mg/Lであった。上澄み水
と沈殿物の比率は9:1であった。
(Example 3) As a powdery substance, Shigaraki red clay, which is a pottery clay produced in Shigaraki Town, Shiga Prefecture, was dried by the method of Example 1,
The water to be treated was treated under the same conditions as in Example 1 except that the pulverized product was used. The water to be treated was separated into precipitates of suspended solids and powdery substances and supernatant water, and the precipitates were deposited at the bottom of the beaker. When the supernatant water was measured with a fluorometer, the transparency was 32 mm. The concentration of suspended solids in the supernatant water was measured and found to be 306 mg / L. The ratio of supernatant water to precipitate was 9: 1.

【0042】(実施例4)粉状物質として、後述の実施
例6の固液分離装置による脱水処理において得られたケ
ーキを実施例1の方法により乾燥し、粒径約5mmの塊
に砕いた再生粉状物質を使用した以外は実施例1と同一
条件で被処理水を処理した。被処理水は浮遊物質および
粉状物質の沈殿物と上澄み水に分離し、沈殿物はビーカ
ー底部に沈殿した。この上澄み水を透視度計で測定した
ところ透視度は82mmであった。また上澄み水中の浮
遊物質濃度を測定したところ98mg/Lであった。
(Example 4) As a powdery substance, the cake obtained by the dehydration treatment by the solid-liquid separation device of Example 6 described later was dried by the method of Example 1 and crushed into lumps having a particle size of about 5 mm. The water to be treated was treated under the same conditions as in Example 1 except that the regenerated powder substance was used. The water to be treated was separated into precipitates of suspended solids and powdery substances and supernatant water, and the precipitates were deposited at the bottom of the beaker. When this supernatant water was measured with a fluorometer, the transparency was 82 mm. The concentration of suspended solids in the supernatant water was measured and found to be 98 mg / L.

【0043】(比較例1)上記被処理水300ccをビ
ーカーに収容して何らの処理もせず5時間静置したとこ
ろ、被処理水はほとんど懸濁したままの状態でわずかに
沈殿が生じており、上澄み水と沈殿物の比率は9.5:
0.5であった。透視度は29mmであり、浮遊物質の
濃度は344mg/Lであった。
(Comparative Example 1) When 300 cc of the water to be treated was placed in a beaker and allowed to stand for 5 hours without any treatment, the water to be treated was slightly suspended with slight precipitation. , The ratio of supernatant water to sediment is 9.5:
It was 0.5. The transparency was 29 mm and the concentration of suspended solids was 344 mg / L.

【0044】(比較例2)粉状物質として市販の粉状無
機系凝集剤であるコスモボンド(商標)を使用した以外
は実施例1と同一条件で被処理水を処理した。被処理水
は浮遊物質および粉状物質の沈殿物と上澄み水に分離
し、沈殿物はビーカー底部に沈殿した。この上澄み水を
透視度計で測定したところ透視度は74mmであった。
また上澄み水中の浮遊物質濃度を測定したところ111
mg/Lであった。上澄み水と沈殿物の比率は8:2で
あった。
Comparative Example 2 The water to be treated was treated under the same conditions as in Example 1 except that a commercially available powdery inorganic flocculant Cosmobond ™ was used as the powdery substance. The water to be treated was separated into precipitates of suspended solids and powdery substances and supernatant water, and the precipitates were deposited at the bottom of the beaker. When this supernatant water was measured with a fluorometer, the transparency was 74 mm.
When the concentration of suspended solids in the supernatant water was measured, it was 111
It was mg / L. The ratio of supernatant water to precipitate was 8: 2.

【0045】(実施例5)実施例1と同一の赤土濁水を
被処理水として使用した。沖縄県の国領マージを採取後
1ヶ月間自然乾燥(天日乾燥)したものを特に粉砕せず
径5mm〜2cm程度の塊状のまま10ccをビーカー
に収容した被処理水300ccに添加し、攪拌混合した
後5時間静置した。被処理水は浮遊物質と赤土の沈殿物
と上澄み水に分離し、沈殿物はビーカー底部に沈殿し
た。この上澄み水を透視度計で測定したところ透視度は
70mmであった。また上澄み水中の浮遊物質濃度を測
定したところ110mg/Lであった。上澄み水と沈殿
物の比率は9:1であった。
(Example 5) The same red soil turbid water as in Example 1 was used as the water to be treated. Naturally dried (sun dried) for 1 month after collecting the national territory merger of Okinawa Prefecture, add 10 cc to the treated water 300 cc in a beaker without stirring and add it to the treated water 300 cc without stirring. After that, it was left to stand for 5 hours. The water to be treated was separated into suspended solids, a red soil precipitate, and supernatant water, and the precipitate settled at the bottom of the beaker. When the supernatant water was measured with a fluorometer, the transparency was 70 mm. The concentration of suspended solids in the supernatant water was measured and found to be 110 mg / L. The ratio of supernatant water to precipitate was 9: 1.

【0046】(実施例6)(株)ナガオカ製除鉄装置
(特願2000−324268号記載の装置と同型のも
の)により京都巨椋ポンプ場地下水を処理した後同装置
の濾材層を逆洗した結果浮遊物質濃度50,000mg
/Lの逆洗排水が生じた。この逆洗排水を被処理水とし
て使用した。粉状物質として実施例1と同一の国領マー
ジから調製した粉状物質を使用した。
(Example 6) An iron removing device manufactured by Nagaoka Co., Ltd. (of the same type as the device described in Japanese Patent Application No. 2000-324268) was used to treat the groundwater of Kyoto Koji pumping station, and then the filter medium layer of the device was backwashed. Concentration of suspended solids 50,000mg
/ L backwash drainage occurred. This backwash drainage was used as water to be treated. As the powdery material, the powdery material prepared from the same national merger as in Example 1 was used.

【0047】この粉状物質10ccをビーカーに収容し
た被処理水300ccに添加し、攪拌混合した後5分間
静置した。被処理水は浮遊物質および粉状物質の沈殿物
と上澄み水に分離し、沈殿物はビーカー底部に沈殿し
た。この上澄み水を透視度計で測定したところ透視度は
35mmであった。また上澄み水中の浮遊物質濃度を測
定したところ274mg/Lであった。上澄み水と沈殿
物の比率は7.5:2.5であった。
10 cc of this powdery substance was added to 300 cc of water to be treated contained in a beaker, and the mixture was stirred and mixed, and then allowed to stand for 5 minutes. The water to be treated was separated into precipitates of suspended solids and powdery substances and supernatant water, and the precipitates were deposited at the bottom of the beaker. When the supernatant water was measured with a fluorometer, the transparency was 35 mm. The concentration of suspended solids in the supernatant water was measured and found to be 274 mg / L. The ratio of supernatant water to precipitate was 7.5: 2.5.

【0048】(実施例7)粉状物質として兵庫県柏原町
産の赤土を実施例1の方法により乾燥、粉砕したものを
使用した以外は実施例6ど同一条件で被処理水を処理し
た。被処理水は浮遊物質および粉状物質の沈殿物と上澄
み水に分離し、沈殿物はビーカー底部に沈殿した。この
上澄み水を透視度計で測定したところ透視度は25mm
であった。また上澄み水中の浮遊物質濃度を測定したと
ころ412mg/Lであった。上澄み水と沈殿物の比率
は7.5:2.5であった。
(Example 7) The treated water was treated under the same conditions as in Example 6 except that the red soil produced in Kashiwara-cho, Hyogo Prefecture was dried and pulverized by the method of Example 1 as a powdery substance. The water to be treated was separated into precipitates of suspended solids and powdery substances and supernatant water, and the precipitates were deposited at the bottom of the beaker. When this clear water was measured with a fluorometer, the transparency was 25 mm.
Met. The concentration of suspended solids in the supernatant water was measured and found to be 412 mg / L. The ratio of supernatant water to precipitate was 7.5: 2.5.

【0049】(実施例8)粉状物質として信楽白土を実
施例1の方法により乾燥、粉砕したものを使用した以外
は実施例6ど同一条件で被処理水を処理した。被処理水
は浮遊物質および粉状物質の沈殿物と上澄み水に分離
し、沈殿物はビーカー底部に沈殿した。この上澄み水を
透視度計で測定したところ透視度は20mmであった。
また上澄み水中の浮遊物質濃度を測定したところ540
mg/Lであった。上澄み水と沈殿物の比率は7.5:
2.5であった。
(Example 8) The water to be treated was treated under the same conditions as in Example 6 except that Shigaraki clay was dried and pulverized by the method of Example 1 as a powdery substance. The water to be treated was separated into precipitates of suspended solids and powdery substances and supernatant water, and the precipitates were deposited at the bottom of the beaker. When the supernatant water was measured with a fluorometer, the transparency was 20 mm.
Moreover, when the concentration of suspended solids in the supernatant water was measured, it was 540
It was mg / L. The ratio of supernatant water to sediment is 7.5:
It was 2.5.

【0050】(比較例3)実施例6の被処理水300c
cをビーカーに収容して何らの処理もせず5分間静置し
たところ、沈殿が生じ、上澄み水と沈殿物の比率は7.
5:2.5であったが、透視度は18mmと低く、浮遊
物質の濃度は618mg/Lであった。
Comparative Example 3 Water to be treated 300c of Example 6
When c was placed in a beaker and allowed to stand for 5 minutes without any treatment, precipitation occurred and the ratio of the supernatant water to the precipitate was 7.
Although it was 5: 2.5, the transparency was as low as 18 mm and the concentration of suspended matter was 618 mg / L.

【0051】(比較例4)粉状物質として市販の粉状無
機系凝集剤であるコスモボンド(商標)を使用した以外
は実施例6と同一条件で被処理水を処理した。被処理水
は浮遊物質および凝集剤の沈殿物と上澄み水に分離し、
沈殿物はビーカー底部に沈殿した。この上澄み水を透視
度計で測定したところ透視度は20mmであった。また
上澄み水中の浮遊物質濃度を測定したところ540mg
/Lであった。上澄み水と沈殿物の比率は6.5:3.
5であった。
Comparative Example 4 The water to be treated was treated under the same conditions as in Example 6 except that a commercially available powdery inorganic flocculant Cosmobond ™ was used as the powdery substance. The water to be treated is separated into suspended matter and flocculant precipitates and supernatant water,
The precipitate settled on the bottom of the beaker. When the supernatant water was measured with a fluorometer, the transparency was 20 mm. Moreover, when the concentration of suspended solids in the supernatant water was measured, it was 540 mg.
It was / L. The ratio of supernatant water to sediment is 6.5: 3.
It was 5.

【0052】水処理における赤土・粘土の凝集剤として
の使用についての考察 実施例1〜8および比較例1〜4を比較すると、赤土の
中で国領マージを乾燥、粉砕したものおよびその再利用
物は沈降速度が最も速く、また上澄み水の透明度および
浮遊物質濃度において最も優れた効果を有することがわ
かる。また国領マージは上澄み水の透明度および浮遊物
質濃度において市販の凝集剤に勝るものであることがわ
かる。また国領マージ以外の赤土も上澄み水の透明度お
よび浮遊物質濃度において市販の凝集剤に勝るものであ
ることがわかる。さらに、粘土である信楽白土を乾燥、
粉砕した粉状物質も上澄み水の透明度および浮遊物質濃
度において市販の凝集剤とほぼ同程度の凝集効果を有す
ることがわかる。
Consideration on Use of Red Soil / Clay as Flocculant in Water Treatment Comparing Examples 1 to 8 and Comparative Examples 1 to 4, dried and crushed Kokuryo merge in red soil and its reused product It has the highest settling rate and has the best effect on the clarity and the suspended matter concentration of the supernatant water. Also, it can be seen that the national territory merger is superior to the commercially available coagulant in the clarity of the clear water and the concentration of suspended solids. In addition, it can be seen that red soil other than the national land merger is superior to the commercially available coagulant in the clarity of the clear water and the concentration of suspended solids. In addition, the clay Shigaraki clay is dried,
It can be seen that the pulverized powdered substance also has almost the same aggregating effect as the commercially available aggregating agent in the clarity of the supernatant water and the concentration of suspended solids.

【0053】2.水処理における赤土・粘土のケーキ形
成助剤としての使用 (実施例9)(株)ナガオカ製除鉄装置(特願2000
−324268号記載の装置と同型のもの)により沖縄
県で発生した赤水を処理した後同装置の濾材層を逆洗し
た結果浮遊物質濃度20,000mg/Lの逆洗排水が
生じた。この逆洗排水を被処理水として使用した。粉状
物質として国領マージを実施例1の方法により乾燥、粉
砕したものを準備した。被処理水1Lと粉状物質1Lを
混合し(混合比1:1)、(株)ナガオカ製210型吸引
式脱水機(米国特許第5,618,424号記載の装置
と同型の装置)を使用して真空吸引による脱水濾過を行
なった。その結果スクリーンドラムの周囲に適度な固さ
の良好なケーキ(含水率55%)が形成される一方25
0mLの濾液が得られた。濾過完了後約30分で濾液内
のスラッジ(粉状物質と浮遊物資の混合物)が沈降し、
沈殿物と上澄み水が約1:1の比率で分離した。上澄み
水中の浮遊物質濃度は150mg/Lであった。
2. Use of Red Soil / Clay as a Cake-Forming Aid in Water Treatment (Example 9) Iron Removal Equipment Made by Nagaoka Co., Ltd.
(The same type as the device described in No. 324268) was used to treat the red water generated in Okinawa Prefecture, and then the filter media layer of the device was backwashed, resulting in backwash drainage with a floating substance concentration of 20,000 mg / L. This backwash drainage was used as water to be treated. As a powdery substance, national merger was dried and pulverized by the method of Example 1 to prepare. 1 L of water to be treated and 1 L of powdery substance were mixed (mixing ratio 1: 1), and a 210 type suction dehydrator manufactured by Nagaoka Co., Ltd. (a device of the same type as the device described in US Pat. No. 5,618,424) was used. It was used for dehydration filtration by vacuum suction. As a result, a good cake (water content 55%) of moderate hardness is formed around the screen drum, while 25
0 mL of filtrate was obtained. Approximately 30 minutes after the completion of filtration, sludge (mixture of powder and suspended matter) in the filtrate settles,
The precipitate and the supernatant water were separated at a ratio of about 1: 1. The concentration of suspended solids in the supernatant water was 150 mg / L.

【0054】(実施例10)粉状物質として、実施例9
において得られたケーキを実施例1の方法により乾燥
し、粒径約5mmに砕いた再生粉状物質を使用した以外
は実施例9と同一条件で被処理水を処理した。その結果
スクリーンドラムの周囲に適度な固さの良好なケーキが
形成される一方650mLの濾液が得られた。濾過完了
後約30分で濾液内のスラッジ(粉状物質と浮遊物資の
混合物)が沈降し、沈殿物と上澄み水が約1:1の比率
で分離した。上澄み水中の浮遊物質濃度は150mg/
Lであった。
Example 10 As a powdery substance, Example 9 was used.
The cake obtained in 1. was dried by the method of Example 1, and the water to be treated was treated under the same conditions as in Example 9 except that the regenerated powder substance crushed to a particle size of about 5 mm was used. As a result, 650 mL of filtrate was obtained while forming a good cake of moderate hardness around the screen drum. About 30 minutes after the completion of filtration, sludge (mixture of powdery substance and suspended solids) in the filtrate settled, and the precipitate and supernatant water were separated at a ratio of about 1: 1. Suspended matter concentration in supernatant water is 150 mg /
It was L.

【0055】(実施例11)(株)ナガオカ製除鉄装置
(特願2000−324268号記載の装置と同型のも
の)により京都巨椋ポンプ場地下水を除鉄処理した後同
装置の濾材層を逆洗した結果浮遊物質濃度50,000
mg/Lの逆洗排水が生じた。この逆洗排水を被処理水
として使用した。粉状物質として兵庫県柏原町産赤土を
実施例1の方法により乾燥、粉砕したものものを使用し
た。被処理水1Lと粉状物質1Lを混合し(混合比1:
1)、(株)ナガオカ製210型吸引式脱水機を使用して
真空吸引による脱水濾過を行なった。その結果スクリー
ンドラムの周囲に適度な固さ(含水率55%)の良好な
ケーキが形成される一方250mLの濾液が得られた。
濾過完了後5分で濾液内のスラッジ(粉状物質と浮遊物
資の混合物)が沈降し、沈殿物と上澄み水が約1:1の
比率で分離した。上澄み水の透視度は45mm、上澄み
水中の浮遊物質濃度は197mg/Lであった。
(Embodiment 11) An iron removing device manufactured by Nagaoka Co., Ltd. (of the same type as the device described in Japanese Patent Application No. 2000-324268) was used to remove iron from groundwater in the Kyoto Koji pumping station, and then the filter medium layer of the device was reversed. As a result of washing, suspended solids concentration 50,000
Backwash drainage of mg / L occurred. This backwash drainage was used as water to be treated. As the powdery substance, red clay produced in Kashiwara-cho, Hyogo Prefecture, which was dried and pulverized by the method of Example 1, was used. 1 L of water to be treated and 1 L of powdery substance were mixed (mixing ratio 1:
1), dehydration filtration by vacuum suction was performed using a 210 type suction dehydrator manufactured by Nagaoka Co., Ltd. As a result, 250 mL of filtrate was obtained while forming a good cake having an appropriate hardness (water content 55%) around the screen drum.
Five minutes after the completion of filtration, sludge (mixture of powdery substances and suspended materials) in the filtrate settled, and the precipitate and supernatant water were separated at a ratio of about 1: 1. The transparency of the supernatant water was 45 mm, and the concentration of suspended substances in the supernatant water was 197 mg / L.

【0056】(比較例5)被処理水2Lに対して粉状物
質1Lを混合(混合比2:1)した以外は実施例9と同
一条件で被処理水を処理した。しかし脱水ケーキは含水
率が過剰で泥状となり、濾液も得られなかった。
Comparative Example 5 The treated water was treated under the same conditions as in Example 9 except that 1 L of the powdery substance was mixed with 2 L of the treated water (mixing ratio 2: 1). However, the dehydrated cake had an excessive water content and became muddy, and a filtrate could not be obtained.

【0057】(実施例12)被処理水として、汚濁した
池の水(砂濾過はしていない)を使用した。この水の浮
遊物質濃度は150mg/Lであった。粉状物質として
国領マージを実施例1の方法により乾燥、粉砕したもの
を準備した。被処理水1Lと粉状物質1Lを混合し(混
合比1:1)、(株)ナガオカ製210型吸引式脱水機を
使用して真空吸引による脱水濾過を行なった。その結果
スクリーンドラムの周囲に適度な固さの良好なケーキが
形成される一方0.2Lの濾液が得られた。濾過完了後
約30分で濾液内のスラッジ(粉状物質と浮遊物資の混
合物)が沈降し、沈殿物と上澄み水が約1:1の比率で
分離した。上澄み水中の浮遊物質濃度は50mg/Lで
あった。また、この処理により、砂濾過では取れなかっ
た色度についても除去することができた。
(Example 12) As the water to be treated, polluted pond water (no sand filtration) was used. The concentration of suspended solids in this water was 150 mg / L. As a powdery substance, national merger was dried and pulverized by the method of Example 1 to prepare. 1 L of the water to be treated and 1 L of the powdery substance were mixed (mixing ratio 1: 1), and dehydration filtration was performed by vacuum suction using a 210 type suction dehydrator manufactured by Nagaoka Co., Ltd. As a result, 0.2 L of filtrate was obtained while forming a good cake of moderate hardness around the screen drum. About 30 minutes after the completion of filtration, sludge (mixture of powdery substance and suspended solids) in the filtrate settled, and the precipitate and supernatant water were separated at a ratio of about 1: 1. The suspended matter concentration in the supernatant water was 50 mg / L. In addition, this treatment also made it possible to remove chromaticity that could not be removed by sand filtration.

【0058】(比較例6)粉状物質として上記汚濁した
水を採取した池の汚泥を実施例1と同一方法により乾
燥、粉砕したものを使用した以外は実施例12と同一条
件で被処理水(汚濁した池の水)を処理した。その結
果、混合汚泥は脱水機のスクリーンドラムに張り付か
ず、固液分離はできなかった。スクリーンを通って吸引
流出した濾液についても上澄み水と沈殿物の分離は生じ
なかった。
(Comparative Example 6) Treated water under the same conditions as in Example 12 except that the sludge in the pond in which the polluted water was sampled as a powdery substance was dried and crushed by the same method as in Example 1 was used. (Polluted pond water) was treated. As a result, the mixed sludge did not stick to the screen drum of the dehydrator, and solid-liquid separation was not possible. With respect to the filtrate sucked out through the screen, separation of supernatant water and precipitate did not occur.

【0059】(比較例7)粉状物質として畑の土を実施
例1と同一方法により乾燥、粉砕したものを使用した以
外は実施例12と同一条件で被処理水(汚濁した池の
水)を処理した。その結果、混合汚泥は脱水機のスクリ
ーンドラムに張り付かず、固液分離はできなかった。ス
クリーンを通って吸引流出した濾液についても上澄み水
と沈殿物の分離は生じなかった。
(Comparative Example 7) Water to be treated (polluted pond water) under the same conditions as in Example 12 except that the soil of a field was dried and pulverized by the same method as in Example 1 as a powdery substance. Was processed. As a result, the mixed sludge did not stick to the screen drum of the dehydrator, and solid-liquid separation was not possible. With respect to the filtrate sucked out through the screen, separation of supernatant water and precipitate did not occur.

【0060】水処理における赤土・粘土のケーキ形成助
剤としての使用についての考察 実施例9〜12および比較例5〜7を比較考察すると、
赤土を乾燥、粉砕した粉状物質は汚泥脱水処理における
ケーキ形成助剤としても従来の凝集剤に劣らぬ効果を有
することがわかる。
Consideration on the Use of Red Soil / Clay as a Cake-Forming Aid in Water Treatment When comparing Examples 9-12 and Comparative Examples 5-7,
It can be seen that the powdery substance obtained by drying and crushing the red soil has an effect comparable to that of the conventional flocculant even as a cake forming aid in sludge dewatering treatment.

【0061】3.汚泥処理における赤土・粘度の使用 (実施例13)粉状物質をケーキ形成助剤として使用し
て汚泥の脱水処理を行った。被処理汚泥として株式会社
ナガオカ工場内で採取した汚泥(廃油の混じったヘド
ロ)を使用した。粉状物質として国領マージを実施例1
の方法により乾燥、粉砕したものを準備した。被処理汚
泥1Lと粉状物質1Lを混合し(混合比1:1)、
(株)ナガオカ製210型吸引式脱水機(米国特許第5,
618,424号記載の装置と同型の装置)を使用して
真空吸引による脱水濾過を行なった。その結果スクリー
ンドラムの周囲に適度な固さの良好なケーキ(含水率8
0%)が形成され、約0.2Lの濾液が得られた。濾過
完了後5分で濾液の表面に油膜が形成され、油膜の下の
濾液内のスラッジ(粉状物質と浮遊物資の混合物)が沈
降し、沈殿物95%と上澄み水5%が得られた。上澄み
水の透視度は5mm、上澄み水中の浮遊物質濃度は20
00mg/Lであった。濾過完了5時間後油膜の下の濾
液はさらに沈殿が進み、上澄み水70%と沈殿物30%
が得られた。上澄み水の透視度は15mm、上澄み水中
の浮遊物質濃度は755mg/Lであった。
3. Use of Red Soil and Viscosity in Sludge Treatment (Example 13) The sludge was dehydrated using a powdery substance as a cake-forming aid. As the sludge to be treated, sludge (sludge mixed with waste oil) collected in Nagaoka Co., Ltd. was used. Example 1 of national land merger as a powdery substance
What was dried and pulverized by the method of 1. was prepared. 1 L of sludge to be treated and 1 L of powdery substance are mixed (mixing ratio 1: 1),
210 type suction dehydrator manufactured by Nagaoka Co., Ltd. (US Pat. No. 5,
Dehydration filtration by vacuum suction was performed using a device of the same type as the device described in No. 618,424). As a result, a good cake (with a moisture content of 8
0%) was formed and about 0.2 L of filtrate was obtained. Five minutes after the completion of filtration, an oil film was formed on the surface of the filtrate, and sludge (mixture of powdery substances and suspended materials) in the filtrate under the oil film was settled, and 95% of precipitate and 5% of supernatant water were obtained. . The clear water has a transparency of 5 mm and the concentration of suspended solids in the clear water is 20.
It was 00 mg / L. 5 hours after the completion of filtration, the filtrate under the oil film was further precipitated, and 70% of the supernatant water and 30% of the precipitate were collected.
was gotten. The transparency of the supernatant water was 15 mm, and the concentration of suspended solids in the supernatant water was 755 mg / L.

【0062】(実施例14)被処理汚泥1Lに対し粉状
物質を2Lを混合(混合被1:2)した以外は実施例1
3と同一方法で汚泥の真空吸引による脱水処理を行っ
た。その結果スクリーンドラムの周囲に適度な固さの良
好なケーキ(含水率60%)が形成され、約0.2Lの
濾液が得られた。濾過完了後5分で濾液の表面に油膜が
形成され、油膜の下の濾液内のスラッジ(粉状物質と浮
遊物資の混合物)が沈降し、沈殿物95%と上澄み水5
%が得られた。上澄み水の透視度は6mm、上澄み水中
の浮遊物質濃度は1600mg/Lであった。濾過完了
5時間後油膜の下の濾液はさらに沈殿が進み、上澄み水
60%と沈殿物40%が得られた。上澄み水の透視度は
50mm、上澄み水中の浮遊物質濃度は178mg/L
であった。
(Example 14) Example 1 except that 1 L of the sludge to be treated was mixed with 2 L of the powdery substance (mixing ratio 1: 2).
In the same manner as in No. 3, the sludge was dehydrated by vacuum suction. As a result, a good cake (water content 60%) having an appropriate hardness was formed around the screen drum, and about 0.2 L of filtrate was obtained. Five minutes after the completion of filtration, an oil film is formed on the surface of the filtrate, and sludge (mixture of powdery substances and suspended materials) in the filtrate below the oil film settles, and 95% of the precipitate and 5
%was gotten. The transparency of the supernatant water was 6 mm, and the concentration of suspended solids in the supernatant water was 1600 mg / L. Five hours after the completion of filtration, the filtrate under the oil film was further precipitated, and 60% of supernatant water and 40% of precipitate were obtained. Clear water has a transparency of 50 mm and the concentration of suspended solids in the clear water is 178 mg / L.
Met.

【0063】(実施例15)実施例13で得たケーキを
乾燥、粉砕したものをケーキ形成助剤として新たな汚泥
の処理に再利用した。被処理汚泥として実施例13と同
一の汚泥(廃油の混じったヘドロ)を使用した。またケ
ーキ形成助剤として実施例13で得たケーキを200℃
で3時間乾燥し、粉砕して得た粉状物質を使用した。被
処理汚泥400ccと粉状物質400ccとを攪拌混合
すると、混合物内で変化が生じ、分離水が出始めた。さ
らに攪拌を約5分間続けて分離水190ccを得た。残
りの混合物を布で絞り10ccの分離水を得た。分離水
の合計は200ccとなった。脱水されたケーキは25
0ccでその含水率は約90%であった。分離水の30分
後の透視度は15mmで浮遊物質濃度は755mg/L
であった(時間をかければ透視度および浮遊物質濃度は
さらに向上すると思われる)。また脱水したケーキの状
態を観察すると、このケーキは乾燥し粉末にすればケー
キ形成助剤として再々使用することができると思われ
る。ケーキおよび沈殿物をケーキ形成助剤として再利用
する場合、上記のとおり被処理汚泥とケーキ形成助剤の
混合物を作っている間に分離水が発生するので、真空吸
引方式で脱水しようとすると混合物がドラムスクリーン
に乗ることが難しく、被処理汚泥の脱水方法としては、
真空吸引方式よりも加圧脱水方式が望ましいことが判っ
た。
(Example 15) The cake obtained in Example 13 was dried and pulverized, and it was reused as a cake-forming aid for the treatment of new sludge. As the sludge to be treated, the same sludge as in Example 13 (sludge mixed with waste oil) was used. In addition, the cake obtained in Example 13 was used as a cake-forming aid at 200 ° C.
The powdery substance obtained by pulverizing after drying for 3 hours was used. When 400 cc of the sludge to be treated and 400 cc of the powdery substance were stirred and mixed, a change occurred in the mixture, and separated water began to come out. Further, stirring was continued for about 5 minutes to obtain 190 cc of separated water. The remaining mixture was squeezed with a cloth to obtain 10 cc of separated water. The total amount of separated water was 200 cc. 25 dehydrated cakes
The water content was about 90% at 0 cc. The transparency of the separated water after 30 minutes is 15 mm and the concentration of suspended matter is 755 mg / L.
(It seems that the transparency and the concentration of suspended solids will be further improved with time.) Further, observing the state of the dehydrated cake, it seems that this cake can be reused again as a cake forming aid if it is dried and powdered. When the cake and precipitate are reused as a cake-forming aid, separated water is generated during the formation of the mixture of the sludge to be treated and the cake-forming aid as described above. Is difficult to ride on the drum screen, and as a method for dewatering the sludge to be treated,
It has been found that the pressure dehydration method is preferable to the vacuum suction method.

【0064】汚泥処理についての考察 実施例13および14から、粉状物質を使用すると、良
好なケーキが形成され、濾液におけるスラッジの沈殿効
果も優れており、粉状物質が従来の凝集剤に劣らず汚泥
脱水の効率的な処理に効果があることがわかる。また、
処理された汚泥のケーキまたは濾液沈殿物も乾燥、粉砕
することによりケーキ形成助剤として再利用できること
がわかる。
Consideration on Sludge Treatment From Examples 13 and 14, the use of the powdery substance formed a good cake and the sludge settling effect in the filtrate was excellent, and the powdery substance was inferior to the conventional flocculant. It can be seen that there is an effect on the efficient treatment of sludge dewatering. Also,
It can be seen that the treated sludge cake or filtrate precipitate can also be reused as a cake-forming aid by drying and grinding.

【0065】[0065]

【発明の効果】以上述べたように、本発明によれば、粉
状物質は被処理水中の浮遊物質を凝集沈降させる凝集剤
としての作用を有し、浮遊物質を濾過槽の濾過層(砂
層)上または容器の底面上に沈殿させ、被処理水を上澄
み水と沈殿物に分離する。したがって、上澄み水のみを
系外に取出すことによって、上澄み水は薬品処理のため
のさらなる処理にかける必要がなく、また濾過槽または
容器に残存する沈殿物は、薬品を含まない赤土または粘
土であるから産業廃棄物としての扱いを受けることなく
容易に処理することができる。
As described above, according to the present invention, the powdery substance has a function as a coagulant for aggregating and suspending the suspended solids in the water to be treated, and the suspended solids are used to filter the suspended solids (sand layer). ) Settle on top or on the bottom of the container to separate the water to be treated into supernatant water and a precipitate. Therefore, by removing only the supernatant water from the system, the supernatant water does not need to be further processed for chemical treatment, and the precipitate remaining in the filter tank or container is chemical-free red clay or clay. Can be easily treated without being treated as industrial waste.

【0066】被処理水または被処理汚泥に粉状物質を添
加して攪拌混合した後この混合物を固液分離装置により
処理してケーキと濾液に分離させ、該濾液を沈殿物と上
澄み水に分離させた後該上澄み水を取出す方法において
は、粉状物質を凝集剤として使用することにより他の凝
集剤を使用しないでも有効に良好なケーキ(含水率が適
度なケーキ)を形成することができ、効率良く汚泥処理
を達成することができる上に、形成されたケーキは薬品
を含有していないので、産業廃棄物としての扱いを受け
ず容易に廃棄処理することができる。
A powdery substance is added to the water to be treated or the sludge to be treated, and the mixture is stirred and mixed, and the mixture is treated with a solid-liquid separator to separate it into a cake and a filtrate, and the filtrate is separated into a precipitate and a supernatant water. In the method of removing the supernatant water after the reaction, a powdery substance can be used as an aggregating agent to effectively form a good cake (a cake having an appropriate water content) without using any other aggregating agent. In addition, sludge treatment can be achieved efficiently, and since the formed cake does not contain chemicals, it can be easily disposed of without being treated as industrial waste.

【0067】また、赤土、粘土および炭化物の少なくと
も1種からなる粉状物質を円筒状スクリーンドラムの外
周にフイルター層として堆積させ水処理を行う方法にお
いても、同様に、粉状物質を凝集剤として使用すること
により他の凝集剤を使用しないでも有効に良好なケーキ
(含水率が適度なケーキ)を形成することができ、効率
良く水処理を達成することができる上に、形成されたケ
ーキは薬品を含有していないので、産業廃棄物としての
扱いを受けず容易に廃棄処理することができる。
Further, also in the method of depositing a powdery substance composed of at least one kind of red clay, clay and carbide as a filter layer on the outer periphery of the cylindrical screen drum to perform water treatment, similarly, the powdery substance is used as an aggregating agent. By using it, it is possible to effectively form a good cake (a cake with an appropriate water content) without using any other flocculant, and it is possible to achieve water treatment efficiently, and the formed cake is Since it contains no chemicals, it can be easily disposed of without being treated as industrial waste.

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

【図1】円筒状スクリーンドラムを使用する実施形態を
模式的に示す断面図で、粉状物質の水溶液を充填した状
態を示す図である。
FIG. 1 is a cross-sectional view schematically showing an embodiment using a cylindrical screen drum, showing a state of being filled with an aqueous solution of a powdery substance.

【図2】円筒状スクリーンドラムの外周にフイルター層
を形成した状態を示す断面図である。
FIG. 2 is a cross-sectional view showing a state in which a filter layer is formed on the outer circumference of a cylindrical screen drum.

【図3】円筒状スクリーンドラムを被処理水中に水没さ
せた状態で連続濾過を行う方法を示す断面図である。
FIG. 3 is a cross-sectional view showing a method of performing continuous filtration with a cylindrical screen drum submerged in water to be treated.

【図4】円筒状スクリーンドラムを被処理水中に半水没
させた状態で連続濾過を行う方法を示す断面図である。
FIG. 4 is a cross-sectional view showing a method of performing continuous filtration in a state where a cylindrical screen drum is submerged in water to be treated.

【符号の説明】[Explanation of symbols]

1 容器 2 水溶液 3 円筒状スクリーンドラム 5 フイルター層 1 container 2 aqueous solution 3 Cylindrical screen drum 5 filter layers

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) B01D 33/44 B01D 33/36 33/58 C02F 11/14 ─────────────────────────────────────────────────── ─── Continued Front Page (51) Int.Cl. 7 Identification Code FI Theme Coat (Reference) B01D 33/44 B01D 33/36 33/58 C02F 11/14

Claims (14)

【特許請求の範囲】[Claims] 【請求項1】赤土および粘土の少なくとも1種を乾燥し
た後粉砕して粉状物質とし、浮遊物質を含有する被処理
水に該粉状物質を添加して攪拌した後所定時間静置する
ことにより浮遊物質を該粉状物質とともに沈降させ、次
いで上澄み水を取出すことを特徴とする、薬品を使用し
ない水処理方法。
1. At least one of red clay and clay is dried and then pulverized into a powdery substance, and the powdery substance is added to water to be treated containing suspended solids, and the mixture is stirred and then allowed to stand for a predetermined time. A method for treating water without using a chemical, characterized in that the suspended substance is allowed to settle with the powdery substance by the method described above, and then the supernatant water is taken out.
【請求項2】請求項1記載の方法により沈降した粉状物
質を取出して再度乾燥した後粉砕して粉状物質として再
利用することを特徴とする、薬品を使用しない水処理方
法。
2. A water treatment method which does not use chemicals, wherein the powdery substance precipitated by the method according to claim 1 is taken out, dried again, and then pulverized for reuse as a powdery substance.
【請求項3】浮遊物資を含有する被処理水に赤土を添加
して攪拌した後所定時間静置することにより浮遊物質を
赤土とともに沈降させ、次いで上澄み水を取出すことを
特徴とする、薬品を使用しない水処理方法。
3. A chemical characterized by adding red soil to water to be treated containing suspended solids, stirring the mixture, and then leaving it to stand for a predetermined time to settle suspended solids together with the red soil, and then removing supernatant water. Unused water treatment method.
【請求項4】赤土および粘土の少なくとも1種を乾燥し
た後粉砕して粉状物質とし、浮遊物質を含有する被処理
水に該粉状物質を添加して攪拌混合した後この混合物を
固液分離装置により処理してケーキと濾液に分離させ、
該濾液を沈殿物と上澄み水に分離させた後該上澄み水を
取出すことを特徴とする、薬品を使用しない水処理方
法。
4. At least one of red clay and clay is dried and then pulverized into a powdery substance, the powdery substance is added to water to be treated containing suspended solids, the mixture is stirred and mixed, and the mixture is solid-liquid. Treated with a separator to separate into cake and filtrate,
A method for treating water without using a chemical, characterized in that the filtrate is separated into a precipitate and supernatant water and then the supernatant water is taken out.
【請求項5】請求項4記載の方法により生成したケーキ
および濾液沈殿物の少なくとも一方を取出して乾燥させ
た後粉砕して粉状物質として再利用することを特徴とす
る、薬品を使用しない水処理方法。
5. Water containing no chemicals, characterized in that at least one of a cake and a filtrate precipitate produced by the method according to claim 4 is taken out, dried and then pulverized for reuse as a powdery substance. Processing method.
【請求項6】赤土および粘土の少なくとも1種を乾燥し
た後粉砕して粉状物質とし、被処理汚泥に該粉状物質を
添加して攪拌混合した後この混合物を固液分離装置によ
り処理してケーキと濾液に分離させ、該濾液を沈殿物と
上澄み水に分離させた後該上澄み水を取出すことを特徴
とする、薬品を使用しない汚泥処理方法。
6. At least one of red soil and clay is dried and then pulverized into a powdery substance, the powdery substance is added to sludge to be treated, and the mixture is stirred and mixed, and then the mixture is treated by a solid-liquid separator. A method for treating sludge without using any chemicals, which comprises separating a cake and a filtrate with a filter, separating the filtrate into a precipitate and supernatant water, and then removing the supernatant water.
【請求項7】請求項6記載の方法により生成したケーキ
および濾液沈殿物の少なくとも一方を取出して乾燥させ
た後粉砕して粉状物質として再利用することを特徴とす
る、薬品を使用しない汚泥処理方法。
7. A sludge free from chemicals, characterized in that at least one of a cake and a filtrate precipitate produced by the method according to claim 6 is taken out, dried and then pulverized for reuse as a powdery substance. Processing method.
【請求項8】赤土、粘土および炭化物の少なくとも1種
を乾燥した後粉砕して粉状物質とし、この粉状物質を水
に溶いて水溶液を調製し、この水溶液中に水没させた円
筒形スクリーンドラムの内側から真空吸引を行うことに
よりスクリーンドラムの外周に該粉状物質から成るフイ
ルター層を予め形成し、このフイルター層が外周に形成
されたスクリーンドラムを被処理水中に水没させた状態
で該スクリーンドラムの該フイルター層の内側から真空
吸引を行うことにより被処理水の濾過を行うことを特徴
とする薬品を使用しない水処理方法。
8. A cylindrical screen in which at least one of red clay, clay and carbide is dried and then pulverized to form a powdery substance, the powdery substance is dissolved in water to prepare an aqueous solution, and the aqueous solution is submerged in the aqueous solution. A filter layer made of the powdery substance is preliminarily formed on the outer periphery of the screen drum by performing vacuum suction from the inside of the drum, and the screen drum having the filter layer formed on the outer periphery is submerged in the water to be treated. A water treatment method using no chemicals, characterized in that the water to be treated is filtered by performing vacuum suction from the inside of the filter layer of the screen drum.
【請求項9】スクリーンドラムを回転させながら請求項
8記載の方法により被処理水の濾過を行い、該スクリー
ンドラムの該フイルター層の外周に形成された濾滓ケー
キ層をスクレーパーにより掻き落として連続濾過を行う
ことを特徴とする薬品を使用しない水処理方法。
9. The water to be treated is filtered by the method according to claim 8 while rotating the screen drum, and the cake cake layer formed on the outer periphery of the filter layer of the screen drum is scraped off by a scraper and continuously. A water treatment method that does not use chemicals characterized by performing filtration.
【請求項10】請求項9記載の方法により掻き落とした
濾滓ケーキを固液分離装置により処理してケーキと濾液
に分離させ、該濾液を沈殿物と上澄み水に分離させた後
該上澄み水を取出すことを特徴とする薬品を使用しない
水処理方法。
10. The cake cake scraped off by the method according to claim 9 is treated with a solid-liquid separator to separate it into a cake and a filtrate, and the filtrate is separated into a precipitate and a supernatant water, and then the supernatant water. A water treatment method that does not use chemicals, which is characterized by taking out water.
【請求項11】赤土、粘土および炭化物の少なくとも1
種を乾燥した後粉砕して粉状物質とし、この粉状物質を
水に溶いて水溶液を調製し、この水溶液中に水没させた
円筒形スクリーンドラムの内側から真空吸引を行うこと
によりスクリーンドラムの外周に該粉状物質から成るフ
イルター層を予め形成し、このフイルター層が外周に形
成されたスクリーンドラムを被処理水中に半水没の状態
で該スクリーンドラムの該フイルター層の内側から真空
吸引を行うことにより被処理水の濾過を行うことを特徴
とする薬品を使用しない水処理方法。
11. At least one of red clay, clay and carbide.
The seeds are dried and then pulverized to form a powdery substance, an aqueous solution is prepared by dissolving this powdery substance in water, and vacuum suction is performed from the inside of the cylindrical screen drum submerged in this aqueous solution so that the screen drum A filter layer made of the powdery substance is preliminarily formed on the outer circumference, and vacuum suction is performed from the inside of the filter layer of the screen drum while the screen drum having the filter layer formed on the outer circumference is submerged in the water to be treated. A water treatment method using no chemicals, which comprises filtering the water to be treated.
【請求項12】スクリーンドラムを回転させながら請求
項11記載の方法により被処理水の濾過を行い、該スク
リーンドラムの該フイルター層の外周に形成された濾滓
ケーキ層を被処理水の上方に設けられたスクレーパーに
より掻き落として脱水ケーキを取出し、連続濾過を行う
ことを特徴とする薬品を使用しない水処理方法。
12. The water to be treated is filtered by the method according to claim 11 while rotating the screen drum, and the cake cake layer formed on the outer periphery of the filter layer of the screen drum is placed above the water to be treated. A water treatment method using no chemicals, which comprises scraping off a dehydrated cake by scraping it with a scraper provided and then performing continuous filtration.
【請求項13】請求項10記載の方法により取出された
ケーキおよび沈殿物を再度乾燥した後粉砕して粉状物資
として再利用することを特徴とする薬品を使用しない水
処理方法。
13. A chemical-free water treatment method characterized in that the cake and the precipitate taken out by the method according to claim 10 are dried again and then pulverized and reused as a powdery material.
【請求項14】請求項12記載の方法により取出された
脱水ケーキを再度乾燥した後粉砕して粉状物資として再
利用することを特徴とする薬品を使用しない水処理方
法。
14. A chemical-free water treatment method, characterized in that the dehydrated cake taken out by the method according to claim 12 is dried again and then pulverized and reused as a powdery material.
JP2001316463A 2001-09-04 2001-10-15 Method for water treatment/sludge treatment without using chemical Pending JP2003154370A (en)

Priority Applications (1)

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Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP2001-267192 2001-09-04
JP2001267192 2001-09-04
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Publication Number Publication Date
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Country Link
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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010131500A (en) * 2008-12-03 2010-06-17 Sumitomo Heavy Ind Ltd Sludge treatment method and sludge treatment apparatus
CN105481213A (en) * 2015-12-16 2016-04-13 温州市兴业市政建设有限公司 Mud-water separation and solidification device
CN107055639A (en) * 2017-04-06 2017-08-18 兰州交通大学 A kind of water stabilization material and preparation method and application method
WO2022120622A1 (en) * 2020-12-09 2022-06-16 唐山圣因海洋科技有限公司 Harbor oil-contaminated chemical wastewater emergency rapid treatment device

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010131500A (en) * 2008-12-03 2010-06-17 Sumitomo Heavy Ind Ltd Sludge treatment method and sludge treatment apparatus
CN105481213A (en) * 2015-12-16 2016-04-13 温州市兴业市政建设有限公司 Mud-water separation and solidification device
CN107055639A (en) * 2017-04-06 2017-08-18 兰州交通大学 A kind of water stabilization material and preparation method and application method
WO2022120622A1 (en) * 2020-12-09 2022-06-16 唐山圣因海洋科技有限公司 Harbor oil-contaminated chemical wastewater emergency rapid treatment device

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