JP4287730B2 - Sludge dewatering method - Google Patents

Sludge dewatering method Download PDF

Info

Publication number
JP4287730B2
JP4287730B2 JP2003371253A JP2003371253A JP4287730B2 JP 4287730 B2 JP4287730 B2 JP 4287730B2 JP 2003371253 A JP2003371253 A JP 2003371253A JP 2003371253 A JP2003371253 A JP 2003371253A JP 4287730 B2 JP4287730 B2 JP 4287730B2
Authority
JP
Japan
Prior art keywords
flocculant
sludge
polymer flocculant
dicyandiamide
amphoteric
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.)
Expired - Fee Related
Application number
JP2003371253A
Other languages
Japanese (ja)
Other versions
JP2005103524A (en
Inventor
裕三 藤島
主 小林
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.)
Hymo Corp
Original Assignee
Hymo Corp
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 Hymo Corp filed Critical Hymo Corp
Priority to JP2003371253A priority Critical patent/JP4287730B2/en
Publication of JP2005103524A publication Critical patent/JP2005103524A/en
Application granted granted Critical
Publication of JP4287730B2 publication Critical patent/JP4287730B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Landscapes

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

Description

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

本発明は、汚泥の脱水方法に関するものであり、詳しくはジシアンジアミド系凝集剤と有機高分子凝集剤とを併用することによる汚泥の脱水方法、特に難脱水性有機汚泥に有効な脱水方法に関する。  The present invention relates to a method for dewatering sludge, and more particularly to a method for dewatering sludge by using a dicyandiamide-based flocculant and an organic polymer flocculant in combination, and in particular, a dewatering method effective for hardly dewaterable organic sludge.

有機高分子凝集剤は、少ない添加量で高い凝集性を示すことから、その開発以来、それまでの無機凝集剤に代わって、廃水中の汚濁物質の凝集や汚泥の濃縮、脱水に多用されるようになり、特に、カチオン性高分子凝集剤が単独で多く使用されてきた。しかしながら、近年、汚泥発生量の増加や汚泥性状の変化に伴う汚泥の難脱水性化が進み、汚泥処理量、脱水ケーキ含水率、SS回収率、ケーキの濾布からの剥離性などの点で、更なる向上が要求されるようになり、カチオン性高分子凝集剤単独では対応が難しくなっている。Organic polymer flocculants exhibit high cohesiveness with a small amount of addition, and since their development, they are frequently used for flocculation of pollutants in sludge, concentration of sludge, and dehydration instead of the conventional inorganic flocculants. In particular, cationic polymer flocculants have been frequently used alone. However, in recent years, sludge has become difficult to dehydrate due to an increase in sludge generation and changes in sludge properties, and in terms of sludge treatment, dehydrated cake moisture content, SS recovery rate, cake peelability from filter cloth, etc. Further improvement is required, and it is difficult to cope with the cationic polymer flocculant alone.

このような状況に対応するため、物性や構造の異なる有機高分子凝集剤を組み合わせて使用する方法が種々提案されている。例えば、カチオン性高分子凝集剤とアニオン性高分子凝集剤と酸性物質を含有する汚泥脱水剤(特公昭63−52527号)、両性高分子凝集剤とアクリレート系カチオン性高分子凝集剤を併用する方法(特開平2−31899号)、ポリアミジン系凝集剤と両性高分子凝集剤を併用する方法(特開平7−223000号)、縮合型ポリアミンカチオン性高分子凝集剤と両性高分子凝集剤を併用する方法(特開2000−225400号)、アニオン性高分子凝集剤と両性高分子凝集剤を併用する方法(特開2003−117600号)など多くの脱水剤や処理方法が開示されている。In order to cope with such a situation, various methods of using organic polymer flocculants having different physical properties and structures in combination have been proposed. For example, a cationic polymer flocculant, an anionic polymer flocculant, and a sludge dewatering agent containing an acidic substance (Japanese Patent Publication No. Sho 63-52527), an amphoteric polymer flocculant and an acrylate cationic polymer flocculant are used in combination. Method (JP-A-2-31899), a method using a polyamidine-based flocculant and an amphoteric polymer flocculant (JP-A-7-223000), a combined polyamine cationic polymer flocculant and an amphoteric polymer flocculant Many dehydrating agents and treatment methods have been disclosed, such as a method for conducting an anionic polymer flocculant and an amphoteric polymer flocculant (Japanese Patent Laid-Open No. 2003-117600).

このように二種以上の有機高分子凝集剤を併用する方法が多く提案されている一方で、無機凝集剤と有機高分子凝集剤とを併用する方法も、依然として多くの提案がなされている。これは、無機凝集剤はカチオン性高分子凝集剤よりも汚泥の中和率を高められる場合が多く、特に難脱水性汚泥の処理に効果を発揮するためと考えられる。例えば、無機凝集剤と両性高分子凝集剤とを併用する方法(特開昭63−158200号、特開平2−180700号、特開平4−59100号、特開平7−256300号など)、無機凝集剤とアニオン性高分子凝集剤と両性高分子凝集剤とを併用する方法(特開平6−134213号、特開2003−251399号)、無機凝集剤とアニオン性高分子凝集剤とを併用する方法(特開平10−57967号、特開2000−185204号)、カチオン性高分子凝集剤と無機凝集剤とを併用する方法(特開平9−24400号、特開2002−166300号)などが開示されている。While many methods for using two or more organic polymer flocculants in combination have been proposed in this manner, many methods for using an inorganic flocculant and an organic polymer flocculant in combination have also been proposed. This is presumably because inorganic flocculants can increase the neutralization rate of sludge more often than cationic polymer flocculants, and are particularly effective in treating hardly dewaterable sludge. For example, a method in which an inorganic flocculant and an amphoteric polymer flocculant are used in combination (Japanese Patent Laid-Open Nos. 63-158200, 2-180700, 4-59100, 7-256300, etc.) Of using an agent, an anionic polymer flocculant, and an amphoteric polymer flocculant (JP-A-6-134213, JP-A-2003-251399), a method of using an inorganic flocculant and an anionic polymer flocculant in combination (JP-A-10-57967, JP-A-2000-185204), a method of using a cationic polymer flocculant and an inorganic flocculant in combination (JP-A-9-24400, JP-A-2002-166300) and the like are disclosed. ing.

しかしながら、無機凝集剤を併用する方法は、難脱水性汚泥に対して脱水性は改善されるが、以下のような種々の問題点を有している。
(1)無機凝集剤の成分は酸性が強く、設備機器類を腐食させる。
(2)汚泥によってはpHが低下し過ぎて、次に添加する高分子凝集剤の性能を低下させるため、中和を必要とする場合があり、操作が複雑となる。
(3)無機凝集剤は添加量が多く、その分脱水ケーキ量が増大するため、廃棄処理コストが上昇する。
(4)汚泥を肥料化する場合に無機凝集剤由来の金属成分が問題となる。
However, although the method using an inorganic flocculant improves the dewaterability of the hardly dewaterable sludge, it has the following various problems.
(1) The inorganic flocculant component is highly acidic and corrodes equipment.
(2) Depending on the sludge, the pH is excessively lowered and the performance of the polymer flocculant to be added next is lowered, so that neutralization may be required, and the operation becomes complicated.
(3) Since the inorganic flocculant is added in a large amount, and the amount of dehydrated cake increases accordingly, the disposal cost increases.
(4) When sludge is fertilized, the metal component derived from the inorganic flocculant becomes a problem.

発明が解決しようとする課題Problems to be solved by the invention

有機性の高い難脱水性の汚泥処理には、無機凝集剤と有機高分子凝集剤、特に両性高分子凝集剤とを併用する方法が効果を発揮するが、無機凝集剤使用に由来する上述のような多くの問題点を有している。本発明は、以上のような従来技術の問題点を解消し、各種汚泥、特に難脱水性有機汚泥を効率的に脱水する方法を提供することを目的とする。A method using a combination of an inorganic flocculant and an organic polymer flocculant, particularly an amphoteric polymer flocculant, is effective for the treatment of highly organic and hardly dewatering sludge. It has many problems. An object of the present invention is to solve the above-mentioned problems of the prior art and to provide a method for efficiently dewatering various sludges, particularly hardly dewatering organic sludge.

課題を解決するための手段Means for solving the problem

無機凝集剤を使用する限り、上述の問題点を解消することは難しく、無機凝集剤に代わる処理剤の検討を種々行った。その結果、多くの処理剤の中からジシアンジアミド系凝集剤の効果に着目し、検討の結果、ジシアンジアミド系凝集剤と有機高分子凝集剤とを併用することにより、本発明の目的を達成できることを見出し、本発明の完成に至った。As long as the inorganic flocculant is used, it is difficult to eliminate the above-mentioned problems, and various investigations of treatment agents in place of the inorganic flocculant were conducted. As a result, focusing on the effect of dicyandiamide type flocculant among many treatment agents, as a result of investigation, it was found that the object of the present invention can be achieved by using dicyandiamide type flocculant and organic polymer flocculant in combination. The present invention has been completed.

すなわち、本発明は、汚泥にジシアンジアミド系凝集剤と両性高分子凝集剤あるいは両性高分子凝集剤に代えてカチオン性高分子凝集剤とアニオン性高分子凝集剤とを順次あるいは同時に添加混合し、脱水する方法に関するものである。なお、ジシアンジアミド系凝集剤を用いた汚泥の脱水に関しては、特開昭54−92572にジシアンジアミド−ホルムアルデヒド縮合系高分子凝集剤とキトサン系カチオン性高分子凝集剤とを併用する方法が開示されているが、それ以外には使用例は見当たらず、本発明の方法は新規な方法ということができる。That is, the present invention is to add a dicyandiamide-based flocculant and an amphoteric polymer flocculant or an amphoteric polymer flocculant to a sludge and add and mix sequentially or simultaneously to dehydrate the sludge. It is about how to do. Regarding the dewatering of sludge using a dicyandiamide-based flocculant, JP-A-54-92572 discloses a method in which a dicyandiamide-formaldehyde condensation polymer flocculant and a chitosan-based cationic polymer flocculant are used in combination. However, there are no other examples of use, and the method of the present invention can be said to be a novel method.

本発明で使用するジシアンジアミド系凝集剤とは、水溶性のジシアンジアミド・ホルムアルデヒド縮合物あるいはジシアンジアミド・ホルムアルデヒド・塩化アンモニウム縮合物である。基本的には、酸あるいはそのアンモニウム塩の存在下で、ジシアンジアミドにホルムアルデヒドを加え、縮合させた生成物であり、水溶液として市販されているものを用いることができる。The dicyandiamide flocculant used in the present invention is a water-soluble dicyandiamide / formaldehyde condensate or dicyandiamide / formaldehyde / ammonium chloride condensate. Basically, a product obtained by adding formaldehyde to dicyandiamide and condensing it in the presence of an acid or an ammonium salt thereof and commercially available as an aqueous solution can be used.

本発明で使用する両性高分子凝集剤としては、アニオン性モノマーとカチオン性モノマーの共重合物、アニオン性モノマーとカチオン性モノマーとノニオン性モノマーの共重合物、あるいはアニオン性モノマーとカチオン性モノマーの共重合物のマンニッヒ変性物またはホフマン分解物などを挙げることができる。具体的には、カチオン性モノマーとしては、ジアルキルアミノアルキルアクリレート、ジアルキルアミノアルキルメタクリレート、ジアルキルアミノアルキルアクリルアミドなどの3級化物あるいは4級化物が挙げられ、例えばジメチルアミノエチルメタクリレート、ジメチルアミノエチルアクリレート、ジメチルアミノプロピルアクリルアミドの3級化物あるいは4級化物が具体例として挙げられるが、これらに限定されない。アニオン性ビニル系モノマーとしては、アクリル酸、メタクリル酸、ビニルスルホン酸、3−メタクリロイルオキシプロパンスルホン酸およびこれらのアルカリ金属塩、アンモニウム塩などが挙げられるが、これらに限定されない。ノニオン性ビニル系モノマーとしては、例えばアクリルアミド、メタクリルアミドなどのビニル基含有アミド類、さらにはビニル基含有ニトリル類、(メタ)アクリル酸のアルキルエステル類などが挙げられるが、これらに限定されない。As the amphoteric polymer flocculant used in the present invention, a copolymer of an anionic monomer and a cationic monomer, a copolymer of an anionic monomer, a cationic monomer and a nonionic monomer, or an anionic monomer and a cationic monomer are used. Mennich modified products or Hoffmann degradation products of the copolymer can be mentioned. Specific examples of the cationic monomer include tertiary or quaternized products such as dialkylaminoalkyl acrylate, dialkylaminoalkyl methacrylate, and dialkylaminoalkyl acrylamide. For example, dimethylaminoethyl methacrylate, dimethylaminoethyl acrylate, dimethyl Specific examples include tertiary or quaternized aminopropylacrylamide, but are not limited thereto. Examples of the anionic vinyl monomer include, but are not limited to, acrylic acid, methacrylic acid, vinyl sulfonic acid, 3-methacryloyloxypropane sulfonic acid, and alkali metal salts and ammonium salts thereof. Examples of nonionic vinyl monomers include, but are not limited to, vinyl group-containing amides such as acrylamide and methacrylamide, vinyl group-containing nitriles, and alkyl esters of (meth) acrylic acid.

本発明で使用するカチオン系高分子凝集剤としては、ジメチルアミノエチル(メタ)アクリレート、ジメチルアミノプロピル(メタ)アクリレートまたはそれらの4級塩もしくは3級塩の単独重合物、あるいはそれらとアクリルアミドまたはメタクリルアミドとの共重合物、ポリアクリルアミドまたはポリメタクリルアミドのホフマン分解物、ポリアミジンなどが挙げられる。Examples of the cationic polymer flocculant used in the present invention include dimethylaminoethyl (meth) acrylate, dimethylaminopropyl (meth) acrylate, a quaternary salt or a homopolymer of the quaternary salt thereof, and acrylamide or methacrylic acid thereof. Examples thereof include a copolymer with amide, a Hoffman degradation product of polyacrylamide or polymethacrylamide, and polyamidine.

本発明で使用するアニオン系高分子凝集剤としては、アクリル酸ナトリウム重合物、アクリル酸ナトリウムまたはメタクリル酸ナトリウムとアクリルアミドまたはメタクリルアミドとの共重合物、アクリルアミド重合物またはメタクリルアミド重合物の部分加水分解物、アクリルアミドまたはメタクリルアミドとアクリル酸ナトリウムまたはメタクリル酸ナトリウムと2−アクリルアミド−2−メチルプロパンスルホン酸ナトリウムの三元共重合物などが挙げられる。Examples of the anionic polymer flocculant used in the present invention include sodium acrylate polymer, copolymer of sodium acrylate or sodium methacrylate and acrylamide or methacrylamide, partial hydrolysis of acrylamide polymer or methacrylamide polymer. And terpolymers of acrylamide or methacrylamide and sodium acrylate or sodium methacrylate and sodium 2-acrylamido-2-methylpropanesulfonate.

本発明において各凝集剤を汚泥に添加する場合、最適な方法は汚泥性状によっても異なるが、一般的にはジシアンジアミド系凝集剤を最初に添加し、続いて有機系高分子凝集剤を添加する方法が好ましい。しかしながら、各凝集剤を同時に添加することも可能である。添加量については、ジシアンジアミド系凝集剤は汚泥に50〜1000ppmを添加することによって効果を発揮するが、より好ましい添加量は100〜600ppmである。また、ジシアンジアミド系凝集剤と両性高分子凝集剤とを用いる場合、その添加量は、重量比で1:0.1〜1:2の範囲が好ましい。ジシアンジアミド系凝集剤とカチオン性高分子凝集剤とアニオン性高分子凝集剤とを用いる場合、その重量比は1:0.1:0.1〜1:2:2の範囲が好ましい。なお、本発明の効果に影響を与えない限り、凝集剤に必要に応じてスルファミン酸その他の添加物を加えることができる。In the present invention, when each flocculant is added to sludge, the optimum method varies depending on the sludge properties, but in general, a dicyandiamide type flocculant is added first, followed by an organic polymer flocculant. Is preferred. However, it is also possible to add each coagulant simultaneously. Regarding the addition amount, the dicyandiamide-based flocculant exhibits an effect by adding 50 to 1000 ppm to the sludge, but a more preferable addition amount is 100 to 600 ppm. Moreover, when using a dicyandiamide type | system | group flocculant and an amphoteric polymer flocculant, the addition amount has the preferable range of 1: 0.1-1: 2 by weight ratio. When a dicyandiamide type flocculant, a cationic polymer flocculant, and an anionic polymer flocculant are used, the weight ratio is preferably in the range of 1: 0.1: 0.1 to 1: 2: 2. As long as the effect of the present invention is not affected, sulfamic acid and other additives can be added to the flocculant as necessary.

以上説明した本発明の方法を種々の汚泥に適用することによって、フロック径が大きく、低含水率で、剥離性に優れた脱水ケーキが得られることを確認した。本発明の方法は、下水や廃水の処理に伴って発生する余剰汚泥、混合汚泥、消化汚泥などの難脱水性有機汚泥の脱水処理に特に有効であり、従来の無機凝集剤を併用する方法と比較して、同程度あるいはそれ以上の効果が得られ、しかも添加量が少なく、操作が容易である特長を有している。By applying the method of the present invention described above to various sludges, it was confirmed that a dehydrated cake having a large floc diameter, a low water content and excellent peelability was obtained. The method of the present invention is particularly effective for the dehydration treatment of hardly dewatering organic sludge such as surplus sludge, mixed sludge, digested sludge, etc. generated in the treatment of sewage and wastewater. In comparison, the same or higher effects can be obtained, and the addition amount is small and the operation is easy.

以下に実施例及び比較例を挙げて本発明をさらに具体的に説明するが、本発明はこれらの例によって限定されるものではない。EXAMPLES Hereinafter, the present invention will be described more specifically with reference to examples and comparative examples, but the present invention is not limited to these examples.

以下の比較例及び実施例には、下記の凝集剤を用いた。
ジシアンジアミド系凝集剤:ジシアンジアミド−ホルムアルデヒド−塩化アンモニウム縮合物55%水溶液(チバ・スペシャルティ・ケミカルズ製 商品名:Zetag7103)
両性高分子凝集剤:メタクリレート系硫酸塩(45)−アクリルアミド(46)−アクリル酸(9)共重合物(カヤフロック(株)商品名D−330E)
カチオン性高分子凝集剤:アクリレート系中カチオン(カヤフロック(株)商品名C−599−1RM)
アニオン性高分子凝集剤:アクリルアミド系中弱アニオン(カヤフロック(株)商品名A−200)
無機凝集剤:ポリ硫酸第二鉄(日鉄鉱業(株)商品名ポリテツ)、ポリ塩化アルミニウム(多木化学(株)商品名PAC260A)
The following flocculants were used in the following comparative examples and examples.
Dicyandiamide flocculant: 55% aqueous solution of dicyandiamide-formaldehyde-ammonium chloride condensate (trade name: Zetag 7103, manufactured by Ciba Specialty Chemicals)
Amphoteric polymer flocculant: methacrylate sulfate (45) -acrylamide (46) -acrylic acid (9) copolymer (trade name D-330E, Kayafloc Co., Ltd.)
Cationic polymer flocculant: acrylate medium cation (Kayafloc Co., Ltd. trade name C-599-1RM)
Anionic polymer flocculant: Acrylamide-based moderately weak anion (Kayaflock Co., Ltd. trade name A-200)
Inorganic flocculants: polyferric sulfate (trade name Polytetsu, Nippon Steel Mining Co., Ltd.), polyaluminum chloride (trade name PAC260A, Taki Chemical Co., Ltd.)

試験用の汚泥としては、と畜場の難脱水性余剰汚泥を用いた。汚泥性状は下記の通りである。
pH:6.25
TS:1.50%
SS:1.41%
VTS:80.7%
Mアルカリ度:440ppm
粗繊維:5.0%
As the test sludge, the hardly dewaterable surplus sludge from the slaughterhouse was used. The sludge properties are as follows.
pH: 6.25
TS: 1.50%
SS: 1.41%
VTS: 80.7%
M alkalinity: 440ppm
Coarse fiber: 5.0%

実施例1
300mlのビーカーに汚泥100mlを採り、撹拌下に所定量のジシアンジアミド系凝集剤(DD)、両性凝集剤(D−330E)を順次添加した後、350rpmで60秒間撹拌した。凝集状態、フロック径を測定後、60メッシュのナイロン製ろ布を敷いたヌッチェ漏斗(ろ過面積20cm)により、ろ過時間とろ液量の関係を測定し、ろ過性を見た。得られたケーキを60メッシュナイロン製ろ布にはさみ、圧搾脱水試験器により、面圧0.5kg/cm2で1分間圧搾した後、ろ布からのケーキの剥離性とケーキ含水率を求めた。なお、DD添加量は300ppmから500ppmまで変え、D−330Eは100ppm一定とした。結果を第1表に示した。フロック径、ろ過速度、ケーキ含水率、剥離性のいずれも極めて良好な結果を示した。
Example 1
100 ml of sludge was taken in a 300 ml beaker, and a predetermined amount of dicyandiamide-based flocculant (DD) and amphoteric flocculant (D-330E) were sequentially added with stirring, followed by stirring at 350 rpm for 60 seconds. After measuring the aggregation state and the floc diameter, the relationship between the filtration time and the filtrate amount was measured with a Nutsche funnel (filtration area 20 cm 2 ) covered with a 60 mesh nylon filter cloth, and the filterability was observed. The obtained cake was sandwiched between 60 mesh nylon filter cloths and squeezed with a pressure dehydration tester at a surface pressure of 0.5 kg / cm 2 for 1 minute, and then the peelability of the cake from the filter cloth and the cake moisture content were determined. The DD addition amount was changed from 300 ppm to 500 ppm, and D-330E was kept constant at 100 ppm. The results are shown in Table 1. The flock diameter, filtration rate, cake moisture content, and peelability all showed very good results.

比較例1
実施例1において、DD添加量を0とした試験を行った。結果を第1表に示した。DDを添加した場合と比較して、脱水性、剥離性いずれも大きく低下した。
Comparative Example 1
In Example 1, a test was conducted with the DD addition amount set to zero. The results are shown in Table 1. Compared with the case where DD was added, both dehydration and peelability were greatly reduced.

実施例2
実施例1において、D−330E添加量を120ppm一定とした以外は同様の試験を行った。結果を第1表に示した。
Example 2
In Example 1, the same test was conducted except that the amount of D-330E added was kept constant at 120 ppm. The results are shown in Table 1.

比較例2
実施例2において、DD添加量を0とした試験を行った。結果を第1表に示した。
Comparative Example 2
In Example 2, a test was conducted with the DD addition amount set to zero. The results are shown in Table 1.

実施例3
実施例1において、D−330E添加量を140ppm一定とした以外は、同様の試験を行った。結果を第1表に示した。両性凝集剤の添加量を増やすと、効果が増大する傾向を示した。
Example 3
In Example 1, the same test was conducted except that the amount of D-330E added was constant at 140 ppm. The results are shown in Table 1. Increasing the amount of amphoteric flocculant tended to increase the effect.

比較例3
実施例3において、DD添加量を0とした試験を行った。結果を第1表に示した。

Figure 0004287730
Comparative Example 3
In Example 3, a test was performed with the DD addition amount set to zero. The results are shown in Table 1.
Figure 0004287730

比較例4
実施例1において、ジシアンジアミド系凝集剤の代わりにポリ塩化アルミニウム(PAC)を用いて同様の試験を行った。PAC添加量を300から3000ppmまで変え、両性凝集剤D−330Eの添加量は100ppm一定とした。結果を第2表に示した。

Figure 0004287730
Comparative Example 4
In Example 1, the same test was performed using polyaluminum chloride (PAC) instead of the dicyandiamide type flocculant. The PAC addition amount was changed from 300 to 3000 ppm, and the addition amount of the amphoteric flocculant D-330E was kept constant at 100 ppm. The results are shown in Table 2.
Figure 0004287730

比較例5
比較例1において、ポリ塩化アルミニウムに変えてポリ硫酸第二鉄(ポリ鉄)を用いて同様の試験を行った。ポリ鉄添加によってpHが低下したものについては苛性ソーダを加え、pH6.0に調整した。結果を第2表に示した。

Figure 0004287730
Comparative Example 5
In Comparative Example 1, the same test was performed using polyferric sulfate (polyiron) instead of polyaluminum chloride. About what the pH fell by polyiron addition, caustic soda was added and it adjusted to pH 6.0. The results are shown in Table 2.
Figure 0004287730

実施例4
実施例1において、両性凝集剤(D−330E)に変えて、カチオン性凝集剤(C−599−1RM)とアニオン性凝集剤(A−200)とスルファミン酸とを重量比で7:2:1に混合溶解した水溶液(CA)を添加した以外は全く同様の試験を行った。結果を第4表に示した。両性凝集剤を用いた場合とほぼ同程度の効果が得られた。

Figure 0004287730
Example 4
In Example 1, instead of the amphoteric flocculant (D-330E), the cationic flocculant (C-599-1RM), the anionic flocculant (A-200), and sulfamic acid were used in a weight ratio of 7: 2: The same test was performed except that the aqueous solution (CA) mixed and dissolved in No. 1 was added. The results are shown in Table 4. The effect was almost the same as when using the amphoteric flocculant.
Figure 0004287730

発明の効果The invention's effect

本発明の方法は、種々の汚泥、特に汚泥処理が困難な有機性の難脱水汚泥に対し、従来の汚泥脱水剤および汚泥処理方法と比較して、凝集フロック径が大きく、ろ過速度、ケーキ含水率、脱水ケーキの剥離性、いずれも極めて良好な効果を示した。無機凝集剤を使用せずに、従来の無機凝集剤と有機高分子凝集剤との併用法と比較して、同等以上の効果を示す有用な方法である。The method of the present invention has a large floc diameter compared to conventional sludge dehydrating agents and sludge treatment methods, various filtration sludges, especially organic difficult-to-dehydrate sludges that are difficult to treat with sludge, filtration rate, cake water content. The rate and the peelability of the dehydrated cake were both very good. This is a useful method that exhibits an effect equal to or higher than that of a conventional method of using an inorganic flocculant and an organic polymer flocculant without using an inorganic flocculant.

Claims (1)

汚泥にジシアンジアミド系凝集剤と両性高分子凝集剤あるいは両性高分子凝集剤に代えてカチオン性高分子凝集剤とアニオン性高分子凝集剤とを順次あるいは同時に添加し、脱水することを特徴とする汚泥の脱水方法。  Sludge characterized by adding a dicyandiamide-based flocculant and an amphoteric polymer flocculant or an amphoteric polymer flocculant sequentially or simultaneously to the sludge for dehydration. Dehydration method.
JP2003371253A 2003-09-26 2003-09-26 Sludge dewatering method Expired - Fee Related JP4287730B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2003371253A JP4287730B2 (en) 2003-09-26 2003-09-26 Sludge dewatering method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2003371253A JP4287730B2 (en) 2003-09-26 2003-09-26 Sludge dewatering method

Publications (2)

Publication Number Publication Date
JP2005103524A JP2005103524A (en) 2005-04-21
JP4287730B2 true JP4287730B2 (en) 2009-07-01

Family

ID=34543946

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2003371253A Expired - Fee Related JP4287730B2 (en) 2003-09-26 2003-09-26 Sludge dewatering method

Country Status (1)

Country Link
JP (1) JP4287730B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110228925A (en) * 2019-06-21 2019-09-13 宁夏三瑞机械环保设备有限公司 A kind of dehydration-type curing agent and preparation method thereof

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3943088B2 (en) * 2004-02-09 2007-07-11 敬一郎 浅岡 Polymer flocculant solution, method for producing the same, and flocculant method using the polymer flocculant solution

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110228925A (en) * 2019-06-21 2019-09-13 宁夏三瑞机械环保设备有限公司 A kind of dehydration-type curing agent and preparation method thereof

Also Published As

Publication number Publication date
JP2005103524A (en) 2005-04-21

Similar Documents

Publication Publication Date Title
JP3097162B2 (en) Sludge dewatering agent and method for dewatering sludge using the same
JP3178224B2 (en) Sludge dewatering agent
JP4287730B2 (en) Sludge dewatering method
JP6134940B2 (en) Coagulation treatment method for oil-containing cleaning wastewater
JP2933627B2 (en) Sludge dewatering method
JPS6144559B2 (en)
JP4149795B2 (en) Sludge dewatering agent
JP4479095B2 (en) Polymer flocculant and sludge dewatering method
JP2962816B2 (en) Flocculant
JP2000015300A (en) Dehydration of sludge
JP3222247B2 (en) Sludge dewatering method
JP3064878B2 (en) Organic sludge treatment
JPH10500A (en) Sludge treatment method
JP5059309B2 (en) Sludge dewatering method
JP3097157B2 (en) Sludge dewatering method
JP6755503B2 (en) Dehydration method of organic sludge
JP3185237B2 (en) Sludge dewatering agent
JPH05269500A (en) Dehydration of sludge
JP3305465B2 (en) Sludge dewatering agent and sludge treatment method using the same
JP2004122081A (en) Method for dehydrating sludge
JPH1085800A (en) Method for dehydrating sludge
JPH1085798A (en) Method for dehydrating sludge
JP2000225400A (en) Method for flocculating/separating suspended particle
JP2006187688A (en) Method for dewatering sludge
JPS6257700A (en) Dehydrating method for sludge

Legal Events

Date Code Title Description
A711 Notification of change in applicant

Free format text: JAPANESE INTERMEDIATE CODE: A711

Effective date: 20060525

A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20060623

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20090226

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20090303

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20090327

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120403

Year of fee payment: 3

R150 Certificate of patent or registration of utility model

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130403

Year of fee payment: 4

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20140403

Year of fee payment: 5

LAPS Cancellation because of no payment of annual fees