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JPH0334399B2 - - Google Patents
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JPH0334399B2 - - Google Patents

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Publication number
JPH0334399B2
JPH0334399B2 JP58130906A JP13090683A JPH0334399B2 JP H0334399 B2 JPH0334399 B2 JP H0334399B2 JP 58130906 A JP58130906 A JP 58130906A JP 13090683 A JP13090683 A JP 13090683A JP H0334399 B2 JPH0334399 B2 JP H0334399B2
Authority
JP
Japan
Prior art keywords
amount
sludge
added
organic polymer
flocculant
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 - Lifetime
Application number
JP58130906A
Other languages
Japanese (ja)
Other versions
JPS6025598A (en
Inventor
Chiaki Igarashi
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.)
Ebara Corp
Original Assignee
Ebara Infilco Co Ltd
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 Ebara Infilco Co Ltd filed Critical Ebara Infilco Co Ltd
Priority to JP58130906A priority Critical patent/JPS6025598A/en
Publication of JPS6025598A publication Critical patent/JPS6025598A/en
Publication of JPH0334399B2 publication Critical patent/JPH0334399B2/ja
Granted legal-status Critical Current

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  • Treatment Of Sludge (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

1 発明の技術分野 本発明は、汚泥の脱水処理に用いる有機高分子
凝集剤の添加量制御方法に関するものである。 2 従来技術の説明 近年、汚泥の脱水助剤として広く用いられてい
る有機高分子凝集剤は、無機系凝集剤と比較して
添加量が少なく脱水ケーキ量が少ない、薬品の取
扱いが容易である、ベルトプレス、遠心分離機等
の高性能脱水機が使用できる等の利点を持つてい
る。 しかしながら、有機高分子凝集剤の添加率には
最適範囲が存在するために、添加量の過少の場合
はもちろん、過多の場合にも脱水状態が良好でな
くなるので、常に何らかの方法で薬品添加量を適
正範囲内に保たなければならないというわずらわ
しさがあつた。 そのために、従来は単位固形物あたりの添加率
を一定とする比例制御方法が用いられてきた。即
ち、汚泥流量と濃度を測定して固形物処理量を求
め、あらかじめ別の手段で求めた最適添加率から
添加量を計算して薬注ポンプ流量を制御する方法
である。この方法は汚泥濃度の変動に対しては、
汚泥濃度計および流量計の信頼性が十分であれば
その後の比例制御そのものは容易であるから、薬
品添加の自動化は可能となるが、現実には濃度計
の信頼性が十分でない。さらに汚泥の質的変動が
あり、最適薬注率が変動する場合は本方法は適用
できない。 実際の汚泥処理では、汚泥の濃度や質の変動に
遭遇する機会が多く、薬品添加の自動化による脱
水操作の最適化制御が困難となる場合が多い。そ
のため、脱水状態を常時観察しながら、添加量を
手動で調節する方法をとらざるを得ず、汚泥処理
コスト全体に占める人件費の割合は極めて大き
い。また、実際の薬品添加率は、適正範囲内であ
つても、どちらかといえば安全サイドである高添
加率側にかたよることは避けられず、薬品費の増
大をきたしている。 3 発明の目的 本発明は、かかる現状に対し、有機高分子凝集
剤を使用する場合に、汚泥の濃度や質の変動に十
分対処できる凝集剤添加量の制御方法を提供し、
薬品費の節減を計るとともに、自動化による人件
費の大幅低減を可能とし、汚泥処理全体のコスト
を低下することを目的とするものである。 4 発明の構成 本発明は、有機高分子凝集剤の添加量と凝集処
理汚泥の毛細管吸引時間の関係を調査し、それら
と脱水ケーキ含水率(以下、ケーキ含水率とい
う)の関係を検討した結果完成されたものであ
り、凝集剤添加量と毛細管吸引時間の関係が、第
2屈曲点となる凝集剤添加量を求め、この該添加
量に0.7以上1.5以上の定数を乗じた量の有機高分
子凝集剤を添加して凝集、脱水処理することを特
徴とするものである。 前記毛細管吸引時間は、海外で汚泥の脱水性の
予測を目的に開発されたものであるが、ここで第
1図により毛細管吸引時間の測定方法の概要につ
いて説明する。吸水性紙1上に金属性の中空円筒
試料受2を立て、この円筒内に一定量の試料を入
れると、円筒底部から試料(懸濁液においてはそ
の母液)は吸水性紙1上に吸収され、同心円を描
きながらA点に達する。この時、電気的に毛細管
吸引時間測定部3が作動し計時が開始され、B点
に達すると計時が停止する。このAB間が試料に
よつて湿潤されるのに要する時間を秒で表わした
ものが前記毛細管吸引時間である。 有機高分子凝集剤の添加量と毛細管吸引時間の
関係を定性的に示すと、第2図のようになる。す
なわち、凝集剤添加量と毛細管吸引時間との関係
を調べると、毛細管吸引時間は、凝集剤添加量の
増加につれて急激に低下したのち屈曲し(この屈
曲点を第1屈曲点という)、特定の区間一定値を
保ち続けたのち、今度は逆に、凝集剤添加量の増
加に伴つて増大し始める(この屈曲点を第2屈曲
点という)ことが明らかとなつた。この第2屈曲
点となる凝集剤添加量を以下、添加量Aと呼ぶこ
とにする。 一方、凝集剤添加量とケーキ含水率の関係は、
第3図のようになる。即ち、添加量の少ない領域
では凝集体の粒径や強度が小さく、ろ布からのし
み出し、はみ出し、はくり不良、重力ろ過部のオ
ーバフロー、スリツトからの流出、等々のために
脱水機の運転が不能となる。添加量が増すにつれ
脱水機の運転が可能となり、ある区間でケーキ含
水率も低下する。しかし、添加量が過多となると
凝集体が分散する傾向があらわれ、脱水性は悪化
する。 第2図と第3図の関係を比較した結果、添加量
Aの近傍が脱水機の運転が良好となり、ケーキ含
水率が低く経済的となる領域であることが明らか
となつた。 数多くの実験結果によれば、第2図に示した毛
細管吸引時間の絶対値や添加量Aの絶対値は、汚
泥の質や凝集剤の種類あるいは脱水機の型式や運
転条件等によつて変化するものの、添加量Aの近
傍が脱水良好な領域となることに変わりはないこ
とが確認されている。また、上記「近傍」の幅は
汚泥の性状、凝集剤の種類、脱水条件等にかかわ
らず0.7A〜1.5Aとなつた。これらの事実から、
添加量Aもしくはその近傍に添加量を調整すれ
ば、脱水機の状態を良好に保つことができる。そ
の際、従来必要であつた汚泥濃度や流量の測定は
不要となる。 ところで、凝集剤添加量と毛細管吸引時間の関
係を求める方法としては、汚泥を採取した後、用
いる脱水機にあつた室内試験方法によつて市販の
装置を用いてバツチ式で実測してもよいが、実機
とは別にモニタラインを設けて汚泥を連続式に採
取し、凝集剤添加量を所定の間隔でかえて毛細管
吸引時間を半連続式に測定できるようにしてもよ
い。また、これらの測定は手動で行なう必要はな
く、適宜自動化してデータ処理装置によつて添加
量Aを求めることもできる。添加量Aは毛細管吸
引時間の添加量による微分値が大きく変化する点
であるから、この微分値を用いて添加量Aを自動
的に求めることもできる。 いずれにせよ、添加量A近傍における添加量と
毛細管吸引時間の関係のみ明らかになれば十分で
ある。既存の自動制御方法を応用して添加量Aを
求めることができる。 かくて添加量Aが求められれば0.7A〜1.5Aの
間で実際の脱水機に供給する汚泥に添加する量を
設定すればよい。汚泥性状の変動速度、脱水機の
応答速度、ケーキ含水率等を加味して設定値を選
定できる。一般的には、添加量Aをそのまま
(1.0A)設定値とすると最も良好かつ経済的な運
転状態となるが、凝集剤を極端に節約したい場合
には0.7A付近に設定し、汚泥の性状変動が厳し
く本発明による制御方式を自動化しても制御の時
間遅れなどの問題が残る場合は1.5Aに近く設定
すればよい。むろん、添加量Aの決定方法の説明
において述べた如く、設定値の選定及び実際の薬
注ポンプの流量制御など、すべて自動制御するこ
とができる。 本発明では凝集剤として、通常市販されている
凝集剤をそのまま利用できる。ここで凝集剤添加
量とは、フロツク形成を行なわしめる凝集剤の添
加量をいい、例えば凝集剤が一種類の場合(この
場合、凝集剤は有機高分子凝集剤である。)はそ
の添加量をいう。複数の場合にはフロツク形成を
担う凝集剤の量をいう。例えば無機凝集剤との併
用の場合には有機高分子凝集剤の量をいい、複数
の有機高分子凝集剤を利用する場合にはフロツク
形成を担う凝集剤の量をいう。 なお、本発明は脱水機として回分式、連続式の
いずれにも、また重力ろ過部を備えたもの、備え
ていないもののいずれにも適用できる。 5 実施例の説明 実施例 1 某下水処理場混合生汚泥(濃度2.5%、PH6.5、
強熱減量68%)を、陽イオン性有機高分子凝集剤
(エバグロースC−123、荏原インフイルコ(株)商品
名、中カチオン)を用いてベルトプレス型脱水機
で脱水した。第1表及び第4図に単位固形物あた
りで示した平均添加率とケーキ含水率、毛細管吸
引時間、添加量A等の結果を示す。
1 Technical Field of the Invention The present invention relates to a method for controlling the amount of an organic polymer flocculant used in sludge dewatering treatment. 2 Description of the prior art In recent years, organic polymer flocculants, which have been widely used as sludge dewatering aids, require less addition than inorganic flocculants, produce less dehydrated cake, and are easier to handle as chemicals. It has the advantage of being able to use high-performance dehydrators such as belt presses and centrifuges. However, since there is an optimal range for the addition rate of organic polymer flocculants, the dehydration condition will not be good if the addition amount is too low or too high, so there is always some way to control the amount of chemicals added. It was a hassle to have to keep it within an appropriate range. For this purpose, a proportional control method has conventionally been used in which the addition rate per unit solid is kept constant. That is, this is a method of measuring the sludge flow rate and concentration to determine the amount of solids treated, and calculating the addition amount from the optimum addition rate determined in advance by another means to control the chemical injection pump flow rate. This method deals with fluctuations in sludge concentration.
If the reliability of the sludge concentration meter and flow meter is sufficient, the subsequent proportional control itself will be easy, and automation of chemical addition will be possible, but in reality, the reliability of the concentration meter is not sufficient. Furthermore, this method cannot be applied if there are qualitative changes in the sludge and the optimal chemical injection rate changes. In actual sludge treatment, there are many opportunities to encounter fluctuations in sludge concentration and quality, and it is often difficult to optimize control of dewatering operations by automating the addition of chemicals. Therefore, it is necessary to constantly monitor the dewatering state and manually adjust the amount added, and labor costs account for an extremely large proportion of the total sludge treatment cost. Further, even if the actual chemical addition rate is within the appropriate range, it is inevitable that the chemical addition rate will be on the safe side, which is a high addition rate, resulting in an increase in chemical costs. 3. Purpose of the Invention In order to address the current situation, the present invention provides a method for controlling the amount of flocculant added that can sufficiently cope with fluctuations in the concentration and quality of sludge when using an organic polymer flocculant.
In addition to cutting down on chemical costs, the aim is to make it possible to significantly reduce labor costs through automation, thereby lowering the overall cost of sludge treatment. 4 Structure of the Invention The present invention was developed as a result of investigating the relationship between the amount of organic polymer flocculant added and the capillary suction time of flocculated sludge, and examining the relationship between them and the moisture content of the dehydrated cake (hereinafter referred to as cake moisture content). The relationship between the amount of flocculant added and the capillary suction time is such that the amount of flocculant added is determined to be the second bending point, and the organic concentration is calculated by multiplying this amount by a constant of 0.7 or more and 1.5 or more. It is characterized by adding a molecular flocculant to perform flocculation and dehydration treatment. The capillary suction time was developed overseas for the purpose of predicting the dehydration properties of sludge, and an overview of the method for measuring the capillary suction time will now be explained with reference to FIG. 1. When a hollow metallic cylindrical sample holder 2 is placed on absorbent paper 1 and a certain amount of sample is put into the cylinder, the sample (or its mother liquor in the case of a suspension) is absorbed onto the absorbent paper 1 from the bottom of the cylinder. and reaches point A while drawing concentric circles. At this time, the capillary suction time measuring section 3 is electrically activated to start timekeeping, and when point B is reached, timekeeping stops. The capillary suction time is the time, expressed in seconds, required for the area AB to be wetted by the sample. The relationship between the amount of organic polymer flocculant added and the capillary suction time is qualitatively shown in FIG. 2. In other words, when examining the relationship between the amount of flocculant added and the capillary suction time, the capillary suction time sharply decreases as the amount of flocculant added increases, then bends (this point of inflection is called the first bending point). It has become clear that after keeping a constant value for a certain period, it begins to increase as the amount of coagulant added increases (this inflection point is referred to as the second inflection point). The amount of coagulant added that corresponds to this second bending point will be referred to as the addition amount A hereinafter. On the other hand, the relationship between the amount of flocculant added and the cake moisture content is
It will look like Figure 3. In other words, in the region where the amount added is small, the particle size and strength of the aggregates are small, causing problems such as seepage from the filter cloth, protrusion, poor peeling, overflow of the gravity filtration section, outflow from the slits, etc., making it difficult to operate the dehydrator. becomes impossible. As the amount added increases, the dehydrator can be operated, and the moisture content of the cake decreases in a certain section. However, if the amount added is too large, the aggregates tend to disperse, resulting in poor dehydration properties. As a result of comparing the relationships in FIG. 2 and FIG. 3, it became clear that the vicinity of the addition amount A is the region where the dehydrator operates well and the cake moisture content is low and economical. According to numerous experimental results, the absolute value of the capillary suction time and the absolute value of the addition amount A shown in Figure 2 change depending on the quality of the sludge, the type of flocculant, the type of dehydrator, operating conditions, etc. However, it has been confirmed that the area around the addition amount A remains a region with good dehydration. Moreover, the width of the above-mentioned "nearby" ranged from 0.7A to 1.5A, regardless of the properties of the sludge, the type of flocculant, the dewatering conditions, etc. From these facts,
If the addition amount is adjusted to the addition amount A or around it, the condition of the dehydrator can be maintained in good condition. At that time, the measurement of sludge concentration and flow rate, which was necessary in the past, becomes unnecessary. By the way, as a method for determining the relationship between the amount of coagulant added and the capillary suction time, it is also possible to collect sludge and then measure it in batches using a commercially available device using a laboratory test method suitable for the dehydrator used. However, a monitor line may be provided separately from the actual machine to continuously collect sludge, and the amount of flocculant added may be changed at predetermined intervals so that the capillary suction time can be measured semi-continuously. Further, these measurements do not need to be performed manually, and the addition amount A can be determined by automation as appropriate using a data processing device. Since the addition amount A is the point at which the differential value of the capillary suction time with respect to the addition amount changes greatly, the addition amount A can also be automatically determined using this differential value. In any case, it is sufficient to clarify only the relationship between the addition amount and the capillary suction time in the vicinity of the addition amount A. The addition amount A can be determined by applying existing automatic control methods. Thus, once the addition amount A is determined, the amount to be added to the sludge to be actually supplied to the dehydrator can be set between 0.7A and 1.5A. Setting values can be selected by taking into consideration the rate of change in sludge properties, response speed of the dehydrator, cake moisture content, etc. In general, the best and most economical operating condition will be obtained if the additive amount A is set as it is (1.0A), but if you want to save the flocculant extremely, set it to around 0.7A to improve the properties of the sludge. If the fluctuation is severe and problems such as control time delay remain even if the control method according to the present invention is automated, it may be set close to 1.5A. Of course, as described in the explanation of the method for determining the addition amount A, the selection of the set value and the actual flow rate control of the chemical injection pump can all be automatically controlled. In the present invention, commercially available flocculants can be used as they are as the flocculant. Here, the amount of flocculant added refers to the amount of flocculant added to form flocs. For example, when there is only one type of flocculant (in this case, the flocculant is an organic polymer flocculant), the amount added. means. If more than one, it refers to the amount of flocculant responsible for floc formation. For example, when used in combination with an inorganic flocculant, it refers to the amount of the organic polymer flocculant, and when multiple organic polymer flocculants are used, it refers to the amount of the flocculant responsible for floc formation. Note that the present invention can be applied to either a batch type or a continuous type dehydrator, and to either a dehydrator with or without a gravity filtration section. 5 Description of Examples Example 1 Mixed raw sludge from a certain sewage treatment plant (concentration 2.5%, PH6.5,
Ignition loss: 68%) was dehydrated using a belt press type dehydrator using a cationic organic polymer flocculant (Evagrowth C-123, Ebara Infilco Co., Ltd. trade name, medium cation). Table 1 and FIG. 4 show the results of the average addition rate per unit solid matter, cake moisture content, capillary suction time, addition amount A, etc.

【表】 本発明によれば、単位固形物あたりで示した添
加量Aは1.0%となり、0.7A〜1.5Aの範囲で脱水
良好となり、しかも1.0Aで最良となることがわ
かる。 実施例 2 某浄水場汚泥(平均濃度5%、PH6.9、強熱減
量65%)を、陰イオン性有機高分子凝集剤(エバ
グロースA152、荏原インフイルコ(株)商品名、中
アニオン)を用いて遠心分離機により脱水した。
本浄水場は天候等により汚泥濃度が大幅に変動す
るため、薬注制御が厄介であり常時凝集剤過剰ぎ
みで運転していた(従来法)。第2表及び第5図
に単位固形物あたりで示した平均添加率とケーキ
含水率、毛細管吸引時間、添加量A等の結果を示
す。
[Table] According to the present invention, the amount A added per unit solid is 1.0%, and it can be seen that good dehydration is achieved in the range of 0.7A to 1.5A, and the best is 1.0A. Example 2 A certain water treatment plant sludge (average concentration 5%, pH 6.9, ignition loss 65%) was treated using an anionic organic polymer flocculant (Evagrowth A152, Ebara Infilco Co., Ltd. trade name, medium anion). and dehydrated using a centrifuge.
At this water treatment plant, the sludge concentration fluctuates significantly depending on weather and other factors, making it difficult to control chemical injection, and the plant was always operated with an excessive amount of coagulant (conventional method). Table 2 and FIG. 5 show the results of the average addition rate per unit solid, cake moisture content, capillary suction time, addition amount A, etc.

【表】 本発明方法の単位固形物あたりで示した添加量
Aは0.09%となり、0.7A〜1.5Aの範囲で脱水処理
が極めて安定し、しかも1.0Aで最良となること
がわかる。また、従来法では脱水機の運転管理に
作業員1名を常駐させる必要があつたが、本発明
ではその必要がなかつた。 このように本発明によれば薬品添加率の減少、
ケーキ含水率の低下、人件費の減少等の効果が認
められる。 実施例 3 某食品工場では、複数の排水処理施設を持ち、
余剰汚染を混合して遠心脱水機により脱水処理し
ていた。製造品種の変動に伴つて余剰汚泥の発生
比率が変動し、有機高分子凝集剤の最適添加率が
変わる。そのため、脱水機の運転時は汚泥濃度、
流量のチエツク以外に最適薬注率のチエツクも実
施する必要があり、かなりの人件費が必要であつ
た。本発明方法を用いると上記チエツクはすべて
不要になり、脱水工程の人工を大幅に削減するこ
とができた。その結果を第3表に示す。
[Table] The amount A added per unit of solid matter in the method of the present invention is 0.09%, and it can be seen that the dehydration treatment is extremely stable in the range of 0.7A to 1.5A, and is best at 1.0A. Further, in the conventional method, it was necessary to have one worker permanently stationed to manage the operation of the dehydrator, but this is not necessary in the present invention. In this way, according to the present invention, the chemical addition rate can be reduced;
Effects such as reduction in cake moisture content and reduction in labor costs are recognized. Example 3 A certain food factory has multiple wastewater treatment facilities.
Excess contamination was mixed and dehydrated using a centrifugal dehydrator. As the production type changes, the generation ratio of surplus sludge changes, and the optimal addition rate of organic polymer flocculant changes. Therefore, when operating the dehydrator, the sludge concentration,
In addition to checking the flow rate, it was also necessary to check the optimum drug injection rate, which required considerable labor costs. By using the method of the present invention, all of the above-mentioned checks are no longer necessary, and the number of manual operations in the dehydration process can be significantly reduced. The results are shown in Table 3.

【表】 ここに、 汚泥濃度……0.9〜1.5% 汚泥 PH……6.5〜7.5 汚泥強熱減量……65〜80 使用凝集剤…… エバグロースC123(荏原イン
フイルコ(株)商品名、DAM系、中カチオン) 6 発明の作用ならびに効果 以上述べた様に、本発明は実際の汚泥脱水処理
において遭遇する汚泥の質や濃度の変動に十分対
処できる有機高分子凝集剤の添加量制御方法であ
り、薬品添加の自動化により脱水工程の最適自動
制御が可能となり、薬品費の低減及び人件費の削
減等の実用上多大な効果をもたらすものである。
[Table] Here, Sludge concentration...0.9~1.5% Sludge PH...6.5~7.5 Sludge ignition loss...65~80 Coagulant used... Evagrowth C123 (Ebara Infilco Co., Ltd. trade name, DAM series, medium) cation) 6 Functions and Effects of the Invention As described above, the present invention is a method for controlling the amount of organic polymer flocculant added that can sufficiently cope with the fluctuations in sludge quality and concentration encountered in actual sludge dewatering treatment. Automation of addition enables optimal automatic control of the dehydration process, which brings great practical effects such as reductions in chemical costs and labor costs.

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

第1図は毛細管吸引時間の測定装置の概略説明
図、第2図は凝集剤添加量と毛細管吸引時間の関
係を定性的に示すグラフ、第3図は凝集剤添加量
とケーキ含水率の関係を定性的に示すグラフ、第
4図及び第5図は本発明の異なる実施例の結果を
示すグラフであつて、いずれも有機高分子凝集剤
の平均添加率とケーキ含水率及び毛細管吸引時間
の関係を示すものである。 1……吸水性紙、2……中空円筒試料受、3…
…毛細管吸引時間測定部。
Figure 1 is a schematic explanatory diagram of the capillary suction time measurement device, Figure 2 is a graph qualitatively showing the relationship between the amount of flocculant added and capillary suction time, and Figure 3 is the relationship between the amount of flocculant added and cake moisture content. Figures 4 and 5 are graphs showing the results of different examples of the present invention, and both show the relationship between the average addition rate of organic polymer flocculant, cake moisture content, and capillary suction time. It shows the relationship. 1...Water absorbent paper, 2...Hollow cylindrical sample holder, 3...
...Capillary suction time measuring section.

Claims (1)

【特許請求の範囲】 1 汚泥に有機高分子凝集剤を添加して凝集、脱
水処理するに際し、有機高分子凝集剤の添加量と
凝集汚泥の毛細管吸引時間との関係が第2屈曲点
となる添加量Aを求め、該添加量Aに0.7以上1.5
以下の定数を乗じて得た値を有機高分子凝集剤の
添加量とすることを特徴とする、有機高分子凝集
剤の添加量制御方法。 2 前記有機高分子凝集剤の添加量を、前記添加
量Aとする特許請求の範囲第1項記載の方法。
[Scope of Claims] 1. When an organic polymer flocculant is added to sludge for flocculation and dewatering treatment, the relationship between the amount of organic polymer flocculant added and the capillary suction time of flocculated sludge becomes a second inflection point. Determine the amount of addition A, and add 0.7 to 1.5 to the amount of addition A.
A method for controlling the amount of an organic polymer flocculant added, the method comprising: setting the amount of the organic polymer flocculant to be a value obtained by multiplying by the following constants. 2. The method according to claim 1, wherein the amount of the organic polymer flocculant added is the amount A.
JP58130906A 1983-07-20 1983-07-20 Addition quantity controlling method for organic high polymeric flocculant Granted JPS6025598A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58130906A JPS6025598A (en) 1983-07-20 1983-07-20 Addition quantity controlling method for organic high polymeric flocculant

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58130906A JPS6025598A (en) 1983-07-20 1983-07-20 Addition quantity controlling method for organic high polymeric flocculant

Publications (2)

Publication Number Publication Date
JPS6025598A JPS6025598A (en) 1985-02-08
JPH0334399B2 true JPH0334399B2 (en) 1991-05-22

Family

ID=15045488

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58130906A Granted JPS6025598A (en) 1983-07-20 1983-07-20 Addition quantity controlling method for organic high polymeric flocculant

Country Status (1)

Country Link
JP (1) JPS6025598A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH04317703A (en) * 1991-04-16 1992-11-09 Kurita Water Ind Ltd Agglomeration processing equipment

Also Published As

Publication number Publication date
JPS6025598A (en) 1985-02-08

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