JP2007301458A - Treatment method of sludge, and fertilizer obtained by the same - Google Patents

Treatment method of sludge, and fertilizer obtained by the same Download PDF

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JP2007301458A
JP2007301458A JP2006131513A JP2006131513A JP2007301458A JP 2007301458 A JP2007301458 A JP 2007301458A JP 2006131513 A JP2006131513 A JP 2006131513A JP 2006131513 A JP2006131513 A JP 2006131513A JP 2007301458 A JP2007301458 A JP 2007301458A
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sludge
weight
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oxide
blue powder
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Tetsuji Ogawa
哲司 小川
Takashi Hanashima
隆志 花嶋
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    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
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    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a treatment method of sludge usefully utilizing the sludge, particularly dredging sludge and blue powder sludge, and a fertilizer obtained by the treatment method. <P>SOLUTION: The sludge is loaded with a flocculant containing at least the following component and weight ratio, agitated and mixed, and separated into a condensate having water and a sludge content as a main component. The flocculant contains silicon dioxide of 15.0 to 35.0 pts.wt., aluminum oxide of 20.0 to 40.0 pts.wt., ferric oxide of 1.0 to 10.0 pts.wt., calcium oxide of 20.0 to 40.0 pts.wt., sodium oxide of 1.0 to 5.0 pts.wt., potassium oxide of 0.1 to 1.2 pts.wt., magnesium oxide of 0.3 to 1.8 pts.wt., phosphoric acid of 0.8 to 2.5 pts.wt., and titanium oxide of 0.01 to 2.0 pts.wt. The sludge is preferably the dredging sludge and the blue powder sludge. The blue powder sludge is preferably obtained by electrolyzing water to be treated containing a blue powder. <P>COPYRIGHT: (C)2008,JPO&INPIT

Description

本発明は、浚渫汚泥や青粉汚泥などの汚泥の処理方法及び該方法により得られた肥料に関する。 The present invention relates to a method for treating sludge such as straw sludge and blue powder sludge, and a fertilizer obtained by the method.

本発明者等は、汚泥に凝集剤を添加処理して砂を製造する方法を開発している(特許文献1)。この方法は、砂を製造するための方法であって肥料等に利用するものではない。
汚泥、例えば浚渫汚泥には、植物の葉などの養分が含まれており、これを肥料などとして利用できれば、汚泥の有効利用に資する。また、青粉は、池や沼などの湖沼に繁殖して水を緑色にする微小な淡水藻であるが、かかる青粉にも栄養分が多量に含まれており、これを肥料として利用できれば、湖沼の水の浄化と併せ、有意義である。
The present inventors have developed a method for producing sand by adding a flocculant to sludge (Patent Document 1). This method is a method for producing sand and is not used for fertilizers.
Sludge, for example, sludge, contains nutrients such as plant leaves. If this can be used as fertilizer, it contributes to effective use of sludge. In addition, blue powder is a small freshwater algae that grows in lakes such as ponds and swamps and turns the water green, but if such blue powder contains a large amount of nutrients and can be used as a fertilizer, This is significant in conjunction with the purification of lake water.

青粉の処理方法として、従来は微生物による処理方法が知られている。この方法は、青粉を含む被処理液に青粉を分解する能力をもつ微生物を投入し、青粉を分解処理する方法であるが、処理に長時間を要し、効率的でない。
ところで、本発明者は被処理水の浄化方法として、高周波交流電圧と直流電圧とを同時に印加して浄水処理する浄水装置を既に開発している(特許文献2)。かかる処理装置を用いて青粉を含む被処理液から青粉と水とを効率よく分離することが望まれていた。
特願2005−259424号 特開2004−130294号公報
As a method for treating blue powder, conventionally, a treatment method using microorganisms is known. This method is a method in which a microorganism having an ability to decompose blue powder is introduced into a liquid to be treated containing blue powder, and the blue powder is decomposed. However, the process takes a long time and is not efficient.
By the way, this inventor has already developed the water purification apparatus which applies a high frequency alternating voltage and a DC voltage simultaneously and purifies water as a purification method of to-be-treated water (patent document 2). It has been desired to efficiently separate blue powder and water from a liquid to be treated containing blue powder using such a processing apparatus.
Japanese Patent Application No. 2005-259424 JP 2004-130294 A

そこで、本発明の目的は、汚泥、特に浚渫汚泥や青粉汚泥の有効利用に資する汚泥の処理方法及び該方法により得られる肥料を提供することにある。 Accordingly, an object of the present invention is to provide a method for treating sludge that contributes to the effective use of sludge, in particular, sludge and blue powder sludge, and a fertilizer obtained by the method.

上記課題を解決するために、本発明による汚泥の処理方法は、汚泥に少なくとも下記成分を下記重量割合で含む凝集剤を添加し攪拌混合して、水と泥分を主成分とする凝集体とに分離すること、を特徴としている。
二酸化珪素15.0〜35.0重量部、酸化アルミニウム20.0〜40.0重量部、酸化第二鉄1.0〜10.0重量部、酸化カルシウム20.0〜40.0重量部、酸化ナトリウム1.0〜5.0重量部、酸化カリウム0.1〜1.2重量部、酸化マグネシウム0.3〜1.8重量部、リン酸0.8〜2.5重量部、酸化チタン0.01〜2.0重量部。
ここで、汚泥として浚渫汚泥を用いるとよい。
また、汚泥は青粉汚泥であり、該青粉汚泥は、青粉を含有する被処理液を電気分解処理して得たものとするとよい。
ここで、電気分解処理は、被処理液を収容した水槽内に3極以上の電極を配し、その電極の内少なくとも2以上の電極間に高周波交流電圧を、前記電極の内少なくとも2以上の電極間に直流電圧を、同時に印加して行うとよい。
また、電極はアルミニウム電極を用いるとよい。
また、本発明による肥料は、上記の汚泥の処理方法により得られた(分離された)泥分を主成分とする凝集体からなるものである。
In order to solve the above-mentioned problems, the sludge treatment method according to the present invention comprises adding a flocculant containing at least the following components in the following weight ratio to the sludge, stirring and mixing, and agglomerates mainly composed of water and mud: It is characterized by being separated.
Silicon dioxide 15.0-35.0 parts by weight, aluminum oxide 20.0-40.0 parts by weight, ferric oxide 1.0-10.0 parts by weight, calcium oxide 20.0-40.0 parts by weight, Sodium oxide 1.0-5.0 parts by weight, potassium oxide 0.1-1.2 parts by weight, magnesium oxide 0.3-1.8 parts by weight, phosphoric acid 0.8-2.5 parts by weight, titanium oxide 0.01 to 2.0 parts by weight.
Here, it is good to use dredged sludge as sludge.
The sludge is blue powder sludge, and the blue powder sludge may be obtained by electrolyzing a liquid to be treated containing blue powder.
Here, in the electrolysis treatment, three or more electrodes are arranged in a water tank containing the liquid to be treated, a high-frequency alternating voltage is applied between at least two of the electrodes, and at least two or more of the electrodes. A DC voltage may be applied between the electrodes at the same time.
Further, an aluminum electrode may be used as the electrode.
Further, the fertilizer according to the present invention is composed of an aggregate mainly composed of (separated) mud obtained by the above-described sludge treatment method.

本発明による汚泥の処理方法によれば、汚泥に所定の組成を有する凝集剤を添加し攪拌混合して、水と泥分を主成分とする凝集体とに分離するようにしたので、水を多量に含んだべちゃべちゃ状態の汚泥を、水と含水率の低い凝集体とに分離することができる。得られた凝集体は、含水率が低く(30〜60%程度)土砂に近い状態であるので、トラックなどに積んで運搬し易く、取り扱いが容易で、有効利用できる。
汚泥として浚渫汚泥を用いると、浚渫汚泥には養分を含むので、得られた凝集体も養分を含み肥料などとして有効に利用することができる。
また、汚泥は青粉汚泥であり、該青粉汚泥は、青粉を含有する被処理液を電気分解処理して得た青粉汚泥とすれば、青粉にも多量の栄養分が含まれているので、青粉汚泥から得られた凝集体は、肥料などとして有効に利用することができる。
電気分解処理によれば、短時間で処理が可能で、効率よく青粉汚泥を得ることができる。ここで、電気分解処理は、水槽内に3極以上の電極を配し、その電極の内少なくとも2以上の電極間に高周波交流電圧を、前記電極の内少なくとも2以上の電極間に直流電圧を、同時に印加して行うようにすれば、交流電圧による電気分解と直流電圧による電気分解との相乗効果により、より効率よく電気分解できる。
また、電極としてアルミニウム電極を用いれば、透明な水と青粉とにきれいに分離でき、青粉を含む被処理液を十分にかつ効率よく浄化できる。
青粉を含む汚れた水をこのように十分にかつ効率よく浄化できるこの方法は、青粉が大量に発生した湖沼の浄化方法として極めて有効で、従来にない画期的な処理方法である。
According to the sludge treatment method of the present invention, a flocculant having a predetermined composition is added to the sludge and mixed by stirring to separate water and agglomerates mainly composed of mud. It is possible to separate a large amount of sludge contained in a large amount into water and an aggregate having a low water content. The obtained agglomerates have a low moisture content (about 30 to 60%) and are in a state close to earth and sand, so that they are easy to carry on a truck or the like, are easy to handle, and can be used effectively.
When dredged sludge is used as sludge, dredged sludge contains nutrients, and thus the obtained agglomerates also contain nutrients and can be used effectively as fertilizers.
The sludge is a blue powder sludge. If the blue powder sludge is a blue powder sludge obtained by electrolyzing a liquid to be treated containing blue powder, the blue powder contains a large amount of nutrients. Therefore, the aggregate obtained from the blue powder sludge can be effectively used as a fertilizer.
According to the electrolysis treatment, the treatment can be performed in a short time, and the blue powder sludge can be obtained efficiently. Here, in the electrolysis treatment, three or more electrodes are arranged in the water tank, a high-frequency AC voltage is applied between at least two of the electrodes, and a DC voltage is applied between at least two of the electrodes. If applied simultaneously, electrolysis can be performed more efficiently due to the synergistic effect of electrolysis using alternating voltage and electrolysis using direct current voltage.
Further, when an aluminum electrode is used as an electrode, it can be cleanly separated into transparent water and blue powder, and the liquid to be treated containing blue powder can be purified sufficiently and efficiently.
This method capable of sufficiently and efficiently purifying dirty water containing blue powder is extremely effective as a purification method for lakes and marshes in which a large amount of blue powder is generated, and is an unprecedented and innovative treatment method.

以下、本発明を実施するための最良の形態を図面を参照しつつ具体的に説明する。図1は電気分解処理装置の概略図、図2は他の例による電気分解処理装置の概略図、図3はビーカー内に収容した被処理液の電気分解前後の様子を示す概略図である。 The best mode for carrying out the present invention will be specifically described below with reference to the drawings. FIG. 1 is a schematic view of an electrolysis treatment apparatus, FIG. 2 is a schematic view of an electrolysis treatment apparatus according to another example, and FIG. 3 is a schematic view showing a state before and after electrolysis of a liquid to be treated contained in a beaker.

本発明による汚泥の処理方法は、汚泥に所定の組成を有する凝集剤を添加し攪拌混合して、水と泥分を主成分とする凝集体とに分離することからなるものである。
汚泥としては浚渫汚泥又は青粉汚泥が好ましい。浚渫汚泥や青粉汚泥には、有機物からなる栄養分が含まれており、かかる汚泥から得られる凝集体もまた栄養分を含むので、肥料として有効に利用することができる。
The sludge treatment method according to the present invention comprises adding a flocculant having a predetermined composition to the sludge, stirring and mixing, and separating into agglomerates mainly composed of water and mud.
As the sludge, straw sludge or blue powder sludge is preferable. The sludge and blue powder sludge contain nutrients made of organic matter, and the aggregates obtained from such sludge also contain nutrients, so that they can be effectively used as fertilizers.

本発明において用いる凝集剤は、少なくとも下記成分を下記重量割合で含むものである。二酸化珪素15.0〜35.0重量部、酸化アルミニウム20.0〜40.0重量部、酸化第二鉄1.0〜10.0重量部、酸化カルシウム20.0〜40.0重量部、酸化ナトリウム1.0〜5.0重量部、酸化カリウム0.1〜1.2重量部、酸化マグネシウム0.3〜1.8重量部、リン酸0.8〜2.5重量部、酸化チタン0.01〜2.0重量部。 The flocculant used in the present invention contains at least the following components in the following weight ratio. Silicon dioxide 15.0-35.0 parts by weight, aluminum oxide 20.0-40.0 parts by weight, ferric oxide 1.0-10.0 parts by weight, calcium oxide 20.0-40.0 parts by weight, Sodium oxide 1.0-5.0 parts by weight, potassium oxide 0.1-1.2 parts by weight, magnesium oxide 0.3-1.8 parts by weight, phosphoric acid 0.8-2.5 parts by weight, titanium oxide 0.01 to 2.0 parts by weight.

より好ましくは、少なくとも下記成分を下記重量割合で含むものである。
二酸化珪素20.0〜30.0重量部、酸化アルミニウム25.0〜35.0重量部、酸化第二鉄2.0〜7.0重量部、酸化カルシウム25.0〜40.0重量部、酸化ナトリウム1.0〜3.0重量部、酸化カリウム0.5〜1.2重量部、酸化マグネシウム0.5〜1.5重量部、リン酸1.0〜2.0重量部、酸化チタン0.05〜1.0重量部。
More preferably, at least the following components are contained in the following weight ratio.
20.0-30.0 parts by weight of silicon dioxide, 25.0-35.0 parts by weight of aluminum oxide, 2.0-7.0 parts by weight of ferric oxide, 25.0-40.0 parts by weight of calcium oxide, Sodium oxide 1.0-3.0 parts by weight, potassium oxide 0.5-1.2 parts by weight, magnesium oxide 0.5-1.5 parts by weight, phosphoric acid 1.0-2.0 parts by weight, titanium oxide 0.05 to 1.0 part by weight.

かかる組成をもつ凝集剤は、汚泥に含まれる泥分を疎水化して凝集させる、即ち、固形分としての泥分が保持する水分量(含水率)の調整を図る水分調整機能(疎水機能)と、凝集された泥分(固形分)に適度な親水性を付与し、残留水分によって硬結晶化させる凝結機能と、凝結した泥分の硬化を促進させる硬化促進機能とを有する。 The flocculant having such a composition has a moisture adjustment function (hydrophobic function) for hydrophobizing and agglomerating the mud contained in the sludge, that is, adjusting the amount of water (moisture content) retained by the mud as a solid content. In addition, the agglomerated mud content (solid content) is imparted with an appropriate hydrophilicity, and has a coagulation function for causing hard crystallization by residual moisture and a curing acceleration function for promoting the curing of the coagulated mud.

本発明において用いる凝集剤は、このような機能をもつため、短時間で効率よく汚泥を凝集させることができる。そして、得られた凝集体は、土砂に近い状態で、取り扱いが容易で、運搬も容易である。
また、本発明において用いる凝集剤は、水に分散させても、ほぼ中性域にあり、分離された水のpHを変化させることがないので、分離された水を処理する際にpH調整等も不要である。
Since the flocculant used in the present invention has such a function, sludge can be efficiently aggregated in a short time. The obtained aggregate is easy to handle and transport in a state close to earth and sand.
Further, the flocculant used in the present invention is almost in the neutral range even when dispersed in water, and does not change the pH of the separated water. Is also unnecessary.

汚泥に添加する凝集剤の添加量は、汚泥(含水率80〜300%)100重量部に対して、凝集剤5〜20重量部の割合で添加する。汚泥の種類や含水率に応じて凝集剤の添加量も上記範囲内において適宜変更する。得られる凝集体の含水率は30〜60%程度である。このようにして得た凝集体は水を含んではいるものの、べちゃべちゃ状態ではなく、固まった状態で、トラックの荷台に積んで運搬することができる。 The amount of the flocculant added to the sludge is 5 to 20 parts by weight of the flocculant with respect to 100 parts by weight of the sludge (water content 80 to 300%). The addition amount of the flocculant is appropriately changed within the above range according to the kind of sludge and the water content. The water content of the obtained aggregate is about 30 to 60%. Although the agglomerates thus obtained contain water, they can be transported by loading them on the truck bed in a solid state rather than a crumbly state.

浚渫汚泥や青粉汚泥には有機物など栄養分が含まれているので、かかる汚泥から得られた凝集体にも栄養分が含まれており、これを肥料として利用することができ、汚泥の有効利用に資する。 浚 渫 Sludge and blue powder sludge contain nutrients such as organic matter, so the agglomerates obtained from such sludge also contain nutrients, which can be used as fertilizer for effective use of sludge. To contribute.

図1は青粉を含有する被処理液の電気分解処理装置を示し、水槽1内には被処理液2が収容され、また、水槽1内には第1電極3a、第2電極3b及び第3電極3cからなる3個の電極が配されている。この内第1電極3aと第2電極3b間には交流高周波電源4から高周波の交流電圧が、第3電極3cと第1電極3a間及び第3電極3cと第2電極3b間には直流電源5から直流電圧が、それぞれ同時に印加される。これにより、それぞれの電極間には直流電流と交流電流が同時に流れ、水槽1内の被処理液2が電気分解されて、青粉が上方に浮上して水と分離される。なお、図1中、符号6はスイッチである。 FIG. 1 shows an electrolysis apparatus for a liquid to be processed containing blue powder. A liquid 2 is stored in a water tank 1, and a first electrode 3a, a second electrode 3b, and a second electrode are stored in the water tank 1. Three electrodes including three electrodes 3c are arranged. A high frequency AC voltage is supplied from the AC high frequency power source 4 between the first electrode 3a and the second electrode 3b, and a DC power source is provided between the third electrode 3c and the first electrode 3a and between the third electrode 3c and the second electrode 3b. A DC voltage from 5 is applied simultaneously. Thereby, a direct current and an alternating current simultaneously flow between the respective electrodes, the liquid 2 to be treated in the water tank 1 is electrolyzed, and the blue powder floats upward and is separated from the water. In FIG. 1, reference numeral 6 denotes a switch.

ここで、交流は60〜250kHzの高周波で30〜110Vの電圧、直流は30〜150Vの電圧条件で電気分解処理を行うのが好ましい。また、電極3a,3b,3cとしては、種々の導電性材料、例えば、チタン、アルミニウム、白金、ステンレス、鉄、黒鉛などが使用可能であるが、青粉を含有する被処理液の電気分解処理には、特にアルミニウムが好ましい。 Here, it is preferable to perform the electrolysis treatment under a high frequency of 60 to 250 kHz with a voltage of 30 to 110 V and a direct current with a voltage of 30 to 150 V. In addition, as the electrodes 3a, 3b, 3c, various conductive materials such as titanium, aluminum, platinum, stainless steel, iron, graphite, etc. can be used, but the electrolysis treatment of the liquid to be treated containing blue powder. In particular, aluminum is preferable.

図2は他の例による電気分解処理装置を示し、水槽1内には被処理液2が収容され、また、2個の交流高周波電源14a,14bと1個の直流電源15をもち、水槽1内には第1電極13a、第2電極13b、第3電極13c及び第4電極13dからなる4個の電極が配されている。この内第1電極13aと第2電極13b間及び第3電極13cと第4電極13d間には交流高周波電源14a,14bから高周波の交流電圧が、第3電極13cと第1電極13a間、第3電極13cと第2電極13b間、第4電極13dと第1電極13a間及び第4電極13dと第2電極13b間には直流電源15から直流電圧が、それぞれ同時に印加される。交流の周波数や電圧、直流電圧、電極等については上述と同様である。 FIG. 2 shows an electrolysis apparatus according to another example, in which a liquid 2 to be treated is accommodated in a water tank 1, two AC high frequency power supplies 14 a and 14 b and one DC power supply 15 are provided. Four electrodes including a first electrode 13a, a second electrode 13b, a third electrode 13c, and a fourth electrode 13d are disposed therein. Among these, between the first electrode 13a and the second electrode 13b, and between the third electrode 13c and the fourth electrode 13d, a high-frequency AC voltage is supplied from the AC high-frequency power sources 14a and 14b, between the third electrode 13c and the first electrode 13a, A DC voltage is simultaneously applied from the DC power source 15 between the third electrode 13c and the second electrode 13b, between the fourth electrode 13d and the first electrode 13a, and between the fourth electrode 13d and the second electrode 13b. The AC frequency, voltage, DC voltage, electrode, etc. are the same as described above.

青粉を含む被処理液の電気分解処理実験
図1に示す電気分解処理装置を用いて、青粉を含む被処理液2の電気分解処理実験を行った。具体的には、1リットルのビーカー(水槽1)に青粉を含んだ被処理液2(掛川市の八ヶ切堀池から採取した)1リットルを入れ、第1電極3a、第2電極3b、第3電極3c共にアルミニウム電極を用い、第1電極3a−第2電極3b間には105kHz、60.5Vの高周波交流電圧を、第3電極3c−第1電極3a間及び第3電極3c−第2電極3b間には102Vの直流電圧を、それぞれ同時に印加して被処理液2の電気分解を行った。このとき、交流側の電流は3.4A、直流側の電流は7.9Aであった。
かかる電気分解処理を3分間行うことにより、当初ビーカー内全体が緑色であった被処理液2(図3(a))は、青粉7が上方に浮上し透明な水8と分離できた(図3(b))。こうして上方に浮上した青粉7を回収し、これを後述する実施例2における青粉汚泥として用いた。
なお、電極としてチタン、白金、ステンレス、鉄などの電極を用いて実験したが、いずれも水は濁った状態で透明には至らず分離が不十分で、アルミニウム電極を用いた場合に、透明な水と青粉とにきれいに分離できた。
Electrolytic treatment experiment of liquid to be treated containing blue powder An electrolysis treatment experiment of liquid to be treated 2 containing blue powder was performed using the electrolysis treatment apparatus shown in FIG. Specifically, 1 liter of a liquid to be treated 2 containing blue powder (collected from Yatsukiri-bori Pond in Kakegawa City) is placed in a 1 liter beaker (water tank 1), and the first electrode 3a, the second electrode 3b, An aluminum electrode is used for both the third electrode 3c, a high-frequency AC voltage of 105 kHz and 60.5 V is applied between the first electrode 3a and the second electrode 3b, the third electrode 3c and the first electrode 3a, and the third electrode 3c and the second electrode 3b. The liquid to be treated 2 was electrolyzed by simultaneously applying a DC voltage of 102 V between the two electrodes 3b. At this time, the AC side current was 3.4 A, and the DC side current was 7.9 A.
By performing such electrolysis treatment for 3 minutes, the liquid 2 to be treated (FIG. 3 (a)), which was initially green in the beaker, could be separated from the transparent water 8 as the blue powder 7 floated upward ( FIG. 3 (b)). Thus, the blue powder 7 that floated upward was collected and used as the blue powder sludge in Example 2 described later.
In addition, although it experimented using electrodes, such as titanium, platinum, stainless steel, and iron, as for an electrode, all are transparent in water, it does not reach transparency, and separation is inadequate, and when an aluminum electrode is used, it is transparent. It was cleanly separated into water and blue powder.

含水率約200%の浚渫汚泥1000kgに凝集剤150kgを添加し、多軸型混合機で攪拌混合して、含水率約50%の凝集体と水とに分離できた。得られた凝集体は、土砂に近い状態で取り扱いが容易で、トラックの荷台に載せて運搬することもできた。
用いた凝集剤の組成は、二酸化珪素22.0重量部、酸化アルミニウム30.0重量部、酸化第二鉄4.0重量部、酸化カルシウム32.0重量部、酸化ナトリウム1.6重量部、酸化カリウム0.8重量部、酸化マグネシウム1.0重量部、リン酸1.5重量部、酸化チタン0.1重量部、その他の成分7.0重量部であった。
150 kg of flocculant was added to 1000 kg of sludge having a water content of about 200%, and the mixture was stirred and mixed with a multi-shaft mixer, and separated into aggregates and water having a water content of about 50%. The obtained agglomerates were easy to handle in a state close to earth and sand, and could be carried on a truck bed.
The composition of the flocculant used was 22.0 parts by weight of silicon dioxide, 30.0 parts by weight of aluminum oxide, 4.0 parts by weight of ferric oxide, 32.0 parts by weight of calcium oxide, 1.6 parts by weight of sodium oxide, It was 0.8 parts by weight of potassium oxide, 1.0 part by weight of magnesium oxide, 1.5 parts by weight of phosphoric acid, 0.1 part by weight of titanium oxide, and 7.0 parts by weight of other components.

含水率約200%の青粉汚泥1kgに凝集剤100gを添加し、攪拌混合して、含水率約50%の凝集体と水とに分離できた。得られた凝集体は、土砂に近い状態で取り扱いが容易で、トラックの荷台に載せて運搬することもできた。用いた凝集剤の組成は、実施例1で用いたものと同じである。 100 g of a flocculant was added to 1 kg of blue powder sludge having a water content of about 200%, and the mixture was stirred and mixed to separate the agglomerate having a water content of about 50% and water. The obtained agglomerates were easy to handle in a state close to earth and sand, and could be carried on a truck bed. The composition of the flocculant used is the same as that used in Example 1.

電気分解処理装置の概略図。Schematic of an electrolysis processing apparatus. 他の例による電気分解処理装置の概略図。The schematic of the electrolysis processing apparatus by another example. ビーカー内に収容した被処理液の電気分解前後の様子を示す概略図。Schematic which shows the mode before and behind electrolysis of the to-be-processed liquid accommodated in the beaker.

符号の説明Explanation of symbols

1 水槽
2 被処理液
3a,13a 第1電極
3b,13b 第2電極
3c,13c 第3電極
13d 第4電極
4,14a,14b 交流高周波電源
5,15 直流電源
6,16 スイッチ
7 青粉
8 透明な水
DESCRIPTION OF SYMBOLS 1 Water tank 2 Liquid to be processed 3a, 13a 1st electrode 3b, 13b 2nd electrode 3c, 13c 3rd electrode 13d 4th electrode 4, 14a, 14b AC high frequency power supply 5,15 DC power supply 6,16 Switch 7 Blue powder 8 Transparent Water

Claims (6)

汚泥に少なくとも下記成分を下記重量割合で含む凝集剤を添加し攪拌混合して、水と泥分を主成分とする凝集体とに分離することを特徴とする汚泥の処理方法。
二酸化珪素15.0〜35.0重量部、酸化アルミニウム20.0〜40.0重量部、酸化第二鉄1.0〜10.0重量部、酸化カルシウム20.0〜40.0重量部、酸化ナトリウム1.0〜5.0重量部、酸化カリウム0.1〜1.2重量部、酸化マグネシウム0.3〜1.8重量部、リン酸0.8〜2.5重量部、酸化チタン0.01〜2.0重量部。
A method for treating sludge, characterized in that a flocculant containing at least the following components in the following weight ratio is added to sludge and mixed by stirring to separate into water and agglomerates mainly composed of mud.
Silicon dioxide 15.0-35.0 parts by weight, aluminum oxide 20.0-40.0 parts by weight, ferric oxide 1.0-10.0 parts by weight, calcium oxide 20.0-40.0 parts by weight, Sodium oxide 1.0-5.0 parts by weight, potassium oxide 0.1-1.2 parts by weight, magnesium oxide 0.3-1.8 parts by weight, phosphoric acid 0.8-2.5 parts by weight, titanium oxide 0.01 to 2.0 parts by weight.
汚泥は浚渫汚泥である請求項1に記載の汚泥の処理方法。 The sludge treatment method according to claim 1, wherein the sludge is dredged sludge. 汚泥は青粉汚泥であり、該青粉汚泥は、青粉を含有する被処理液を電気分解処理して得たものである請求項1に記載の汚泥の処理方法。 The sludge treatment method according to claim 1, wherein the sludge is blue powder sludge, and the blue powder sludge is obtained by electrolyzing a liquid to be treated containing blue powder. 電気分解処理は、被処理液を収容した水槽内に3極以上の電極を配し、その電極の内少なくとも2以上の電極間に高周波交流電圧を、前記電極の内少なくとも2以上の電極間に直流電圧を、同時に印加して行う請求項3に記載の汚泥の処理方法。 In the electrolysis treatment, three or more electrodes are arranged in a water tank containing a liquid to be treated, a high-frequency alternating voltage is applied between at least two of the electrodes, and a high-frequency alternating voltage is applied between at least two of the electrodes. The method for treating sludge according to claim 3, wherein a direct current voltage is applied simultaneously. 電極はアルミニウム電極を用いる請求項4に記載の汚泥の処理方法。 The sludge treatment method according to claim 4, wherein the electrode is an aluminum electrode. 請求項2乃至5のいずれか1項に記載の汚泥の処理方法により得られた泥分を主成分とする凝集体からなる肥料。 The fertilizer which consists of the aggregate which has as a main component the mud obtained by the processing method of the sludge of any one of Claim 2 thru | or 5.
JP2006131513A 2006-05-10 2006-05-10 Treatment method of sludge, and fertilizer obtained by the same Pending JP2007301458A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101268376B1 (en) 2012-12-18 2013-05-28 제일산업개발(주) Composition for coagulant

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101268376B1 (en) 2012-12-18 2013-05-28 제일산업개발(주) Composition for coagulant

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