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JPS5867399A - Dehydrating agent and using method - Google Patents

Dehydrating agent and using method

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Publication number
JPS5867399A
JPS5867399A JP56167679A JP16767981A JPS5867399A JP S5867399 A JPS5867399 A JP S5867399A JP 56167679 A JP56167679 A JP 56167679A JP 16767981 A JP16767981 A JP 16767981A JP S5867399 A JPS5867399 A JP S5867399A
Authority
JP
Japan
Prior art keywords
sludge
org
dehydrating agent
humus
organic
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
JP56167679A
Other languages
Japanese (ja)
Inventor
Takehiko Kano
鹿野 武彦
Hiroshi Nagayama
永山 広
Toshio Yugawa
湯川 俊夫
Masuo Honda
本多 益男
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.)
Sanyo Chemical Industries Ltd
Original Assignee
Sanyo Chemical Industries 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 Sanyo Chemical Industries Ltd filed Critical Sanyo Chemical Industries Ltd
Priority to JP56167679A priority Critical patent/JPS5867399A/en
Publication of JPS5867399A publication Critical patent/JPS5867399A/en
Pending legal-status Critical Current

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  • Treatment Of Sludge (AREA)

Abstract

PURPOSE:To provide a marked synergistic effect and to obtain a dehydrating agent having excellent solid-liquid separating performance for org. sludge by combining humus (humus soil) and org. polymer flocculating agents. CONSTITUTION:The above-described dehydrating agent is formed by combining humus (or humus soil) (e.g.; grass peat, materials resembling to grass peats) and org. polymer floculating agents. Cationic polymer flocculating agents, more particularly salt (co)polymers of tertiary nitrogen-contg. (meth)acrylate and acids, etc. are preferable for the polymer flocculating agents. The quantity of the humus to be added per solids weight of the org. sludge is usually 2-80%, more particularly 5-70%, and that of the org. polymer flocculating agents about 0.05-2%, more particularly 0.1-1%. The org. sludge is sewage, night soil or the sludge produced by activated sludge treatment of such materials. The quantity of the dehydrating agent to be used in the stage of solid-liquid sepn., filtration and dehydration by using said dehydrating agent is usually 2-80%, more preferably 5-70% per solids weight of the org. sludge.

Description

【発明の詳細な説明】 本発明は脱水剤および使用法fこ関するものである。[Detailed description of the invention] The present invention relates to dehydrating agents and methods of use.

従来より有機性汚泥たとえば下水、し尿などの余剰汚泥
を脱水処理する場合、無機系の塩化第二鉄(塙鉄)や消
石灰(石灰)などを併用または単独使用し、真空式脱水
機(オリバー脱水機など)で脱水処理し、得られるケー
キを焼却するいわゆる地鉄石灰法が主流であった。しか
し塙鉄石灰法は多量の石灰を使用する(たとえば地鉄5
%、石灰30%)ため、脱離孜のPHは11〜12位に
上がりそれを中7FDするため多量の酸を必要としたり
また、脱水処理されたケーキを焼却する場合、ケーキ中
の地鉄9石灰は自大黙せずかつケーキの嵐は35%もふ
えるため、焼却に必要な燃料費が多くか−るなどの欠点
かある。また高分子凝集剤単独では真空式脱水機の場合
、脱水できにくいという欠点がある。
Traditionally, when dehydrating organic sludge, such as sewage or human waste, surplus sludge, such as sewage or human waste, has been dehydrated by using inorganic ferric chloride (Hanwa Tetsu) or slaked lime (lime) together or alone. The mainstream was the so-called jitetsu-lime method, which involved dehydration using a machine (such as a machine) and incineration of the resulting cake. However, the Hanawa Tetsu lime method uses a large amount of lime (for example, Jitetsu 5
%, lime 30%), the PH of the dehydrated water rises to 11 to 12, and a large amount of acid is required to perform medium 7FD. 9 Lime does not hold back and the cake storm increases by 35%, so there are disadvantages such as the increased fuel cost for incineration. Furthermore, when using a polymer flocculant alone, there is a drawback that dehydration is difficult in the case of a vacuum dehydrator.

一方、微粉炭と高分子凝集Aすを併用して有機性汚泥を
脱水処理する方法もあるが、この場合、微粉炭と有機性
汚泥とは高分子凝集剤に対して反応速度がそれぞれ異な
り、微粉炭のみが高分子凝集剤と早く反応してしまうた
め、本来の目的である有機性汚泥のj逸水には効果を十
分に発揮できない欠点がある。
On the other hand, there is a method of dehydrating organic sludge using a combination of pulverized coal and polymer flocculant, but in this case, pulverized coal and organic sludge have different reaction rates with respect to the polymer flocculant. Since only pulverized coal reacts quickly with the polymer flocculant, it has the disadvantage that it cannot be fully effective in removing water from organic sludge, which is the original purpose.

本発明省らは上記の点tこ笛、磁して、新たに’74 
ha質の特長を生かし、これと有機系高分子凝集剤とを
組合せた脱水剤を使1月し、有機性汚泥を処理したとこ
ろ、著しい相乗効果かあることを見出し本発明に到達し
た。
The Ministry of Invention et al.
When organic sludge was treated using a dehydrating agent that took advantage of the characteristics of HA and an organic polymer flocculant, it was discovered that there was a significant synergistic effect, and the present invention was achieved.

すなわち本発明は’?441目口および冶゛機系1「、
1分子d栗剤を組合せてなる有機性IIJ泥の固液外1
iJll性能のすぐれた脱水剤(第一発明)お」:O・
有機jY+:、i/j泥に腐植質を添加し、次いて有機
系高分子凝集剤を添加し、固液分趨口:を行うことを特
徴とする脱水剤の使用法(第二発明)である。
In other words, the present invention is '? 441 Eye opening and machine system 1
Solid-liquid organic IIJ mud made by combining 1 molecule D chestnut agent 1
Dehydrating agent with excellent iJll performance (first invention)
Method for using a dehydrating agent characterized by adding humus to organic jY+:, i/j mud, then adding an organic polymer flocculant, and performing solid-liquid separation (second invention) It is.

本発明における腐植質に1−たは腐1“1土)としては
草炭および草炭類似物質かあげられる。
In the present invention, the humus (or humus) includes grass charcoal and grass charcoal-like substances.

草炭としては化学大1Y與5.第50】頁、(昭和38
年11月、共立出版株式公ネ1゛定行)に記載されてい
るものがあげられる。具体的に1.t 、:、スコケ(
ミズコ゛ケ科)、ヨシ、スケ、力λ・(イネ不ご1)、
その他ヤナギ、シャクナケなとの低木か長年月をこわt
こり凍結枯死、残留してタイ積重に/1°ったものでJ
)また草炭類似物質としてはりポナーセ1−R」にンー
Wh A 判内業陣餐昂)かihげらソ1.る。これは
合体またはその・池の(共)重合1本たとえば3級窒累
含有ビニル単量体単位を有する水溶性ビニル(共)重合
体〔3級窒系含有(メタ)アクリレートもしくは(メタ
)アタリルアミドまたはこれらと酸との塩(共)重合体
など〕;4級窒5に含有ビ・iこ71)め(アられろ。
As for the grass charcoal, it is 5. No. 50] page, (Showa 38
Examples include those listed in Kyoritsu Shuppan Co., Ltd. 1. Specifically 1. t, :, Skoke (
Sphagnumaceae), Reed, Suke, Power λ・(Rice Fuggo 1),
Other shrubs such as willows and rhododendrons have been afraid of the moon for many years.
J
) Also, as a substance similar to grass charcoal, it has been used as a substance similar to Hariponase 1-R. Ru. This is a combination of water-soluble vinyl (co)polymers having tertiary nitrogen-containing vinyl monomer units [tertiary nitrogen-containing (meth)acrylates or (meth)atalylamides]. or a salt (co)polymer of these and an acid];

これらのうち好ましいものは3級窒紫含有(メタ)アク
リレートもしくは(メタ)アクリルアミドと酸とのJj
、r(共)〕111合および4上記において(共)重合
体とは重合体または/および共重合体を、(メタ)アク
リレ・−1・とけアクリレ・−1−まtこは/お3(二
びメタアクリレ−1・を示し他の記載もこれと同様の黄
味をボす。
Among these, preferred are tertiary nitrogen-purple-containing (meth)acrylates or (meth)acrylamide and acid Jj
. (Methacrylate 1.) Other descriptions also have a similar yellow tinge.

場合により、カシ−オン性高分子b5(1束剤と他の有
機系高分子凝集剤を(Jf’ IIJすることムできる
。他の他の有機系高分子凝集剤のijtはカチオン性高
分子上記の有機系高分子凝集剤の分子量は通常4vO万
〜1000万、好ましくは400万〜600万である。
In some cases, a cationic polymer b5 (1) and another organic polymer flocculant (Jf' IIJ) can be combined. The molecular weight of the above organic polymer flocculant is usually 4vO to 10,000,000, preferably 4,000,000 to 6,000,000.

本発明の脱水剤において’/A qiljl賀と有機系
高分子凝集剤の量は種々変えることかできるか、有機性
汚泥の固形分車駕当りの添加11(として11へAII
F ’c′■が通量2〜80%、好ましくは5〜70%
であり、有機系本発明における有機性汚泥としては下水
9し尿などまたはこれを活性汚泥処理または消化汚泥処
理したものおよび食品廃水から生じ1こ汚泥などがあげ
られる。
In the dehydrating agent of the present invention, the amount of organic polymer flocculant and organic polymer flocculant can be varied.
F'c'■ is 2 to 80%, preferably 5 to 70%
Examples of the organic sludge in the present invention include sewage human waste, activated sludge treated or digested sludge treated sewage, and sludge produced from food wastewater.

本発明の脱水剤を用いて固液7分離、濾過脱水するに際
し、脱水剤の使用竜は有機性汚泥の固型分重量あたり通
常2〜80%、好ましくは5〜70%である。
When performing solid-liquid separation and filtration dehydration using the dehydrating agent of the present invention, the amount of dehydrating agent used is usually 2 to 80%, preferably 5 to 70%, based on the solid weight of the organic sludge.

本発明の脱水剤を有機性汚泥に添加する(こ際し腐植質
はそのま5または5〜50重量%程度の水スラリーとし
て添加される。有機系高分子凝集剤は通常01〜1 重
量%程度の水溶液として添加される。
The dehydrating agent of the present invention is added to the organic sludge (at this time, the humus is added as is or as an aqueous slurry of about 5 to 50% by weight.The organic polymer flocculant is usually added to the organic sludge at about 0.1 to 1% by weight). It is added as an aqueous solution.

添加においては有機性汚泥に腐植質を添加し攪拌、次い
で濾過脱水を行うが濾過脱水を行う場合の脱水機として
は真空脱水機1ことえばオリバーフイルター、ベル!・
フィルター、1、うl、フィルター 。
In addition, humus is added to organic sludge, stirred, and then filtered and dehydrated.The dehydrator used for filtration and dehydration is a vacuum dehydrator, such as an Oliver filter or a Bell!・
filter, 1, ul, filter.

グリコ−1〜フイルターなどかJ’)げられる。これら
分子凝集剤」(大森英三名、昭和50q: 1月、高分
子刊行会発行)の第131頁に記載されている。真空脱
水板以外に遠心脱水機90−ルプレス型ベルト脱水機な
とも使用できる。
Glyco-1~filter etc.J') can be obtained. These Molecular Flocculants" (Eizo Omori, January 1975, published by Kobunshi Kankai), page 131. In addition to vacuum dehydration plates, centrifugal dehydrators and 90-le-press type belt dehydrators can also be used.

泊過脱水により得られたケー・1は公知の方法で焼却な
とされる3゜ 本発明の脱水剤には必留かΔリフ1.ば本発明U)効果
を阻害しない範囲でポリj7ut化アiチ、 f+lf
 l□1ツバノ」−硫酸第一鉄、塩化第二鉄、消石灰4
■どのツ+!(機系凝集剤を併用してもよい。その量は
有j12−(性7tj泥の固形分重量当り通常01〜5
 %、μr〕にしく 1.i、 O,i = 3%であ
る。
The K-1 obtained by over-dehydration must be incinerated by a known method.Is the dehydrating agent of the present invention necessarily retained? According to the present invention U) polyj7ut is added within a range that does not impede the effect, f+lf
l□1 Tsubano” - ferrous sulfate, ferric chloride, slaked lime 4
■What Tsu+! (A mechanical flocculant may also be used in combination.The amount is usually 0.1 to 5.0% per solid weight of the mud.
%, μr] 1. i, O, i = 3%.

本発明の脱水剤は下記の効果を夕する。The dehydrating agent of the present invention has the following effects.

(])脱水性が良好で71’) り 、脱水後の流失S
、S(けん濁物質)か少ない。具体的にはj1鴇植質と
有機系高分子υI集剤を有機性l’i泥(こ加えた場合
p6植為 質と有機系高分子凝集剤との反応はおそく、有機性汚泥
と有機系高分子凝集剤との反応と同じ位であるため有機
性汚泥の脱水性に影響しない。−万機粉炭と有機系高分
子凝集剤を使用する場合、微粉炭と有機系高分子凝集剤
の反応が有機性汚泥と付根系高分子凝集剤の反応よりも
早いため、汚泥の脱水に十分効果を発111fでき11
まfコ有機性汚泥の1・脱水性にバラツキかでき、また
涙液中にS、Sが流失しXきれいなP液が得らtl、な
い。そのためには再度処理する必要かある。
(]) Good dehydration properties71')
, S (suspended substance) or less. Specifically, when J1 plant material and organic polymer υI flocculant are added to organic l'i mud, the reaction between p6 plant material and organic polymer flocculant is slow, and organic sludge and organic It does not affect the dewatering performance of organic sludge because the reaction is about the same as the reaction with the organic polymer flocculant. - When using pulverized coal and organic polymer flocculant, the Because the reaction is faster than the reaction between organic sludge and root-based polymer flocculant, it is highly effective in dewatering sludge.
1. The dehydration properties of organic sludge vary, and S and S are washed away into the lachrymal fluid, making it impossible to obtain a clean P fluid. To do so, it may be necessary to process it again.

低いケーキか得られる。質値質0)添加量をふやしてい
っても炉布とのハクlJiは良好である。
A low cake is obtained. Quality value Quality 0) Even if the amount added is increased, the peeling strength with the furnace cloth is good.

(3)脱離液のPHは無機系の凝集剤を使用しないため
、高くなく、中和を必要としない。
(3) Since no inorganic flocculant is used, the pH of the desorbed solution is not high and does not require neutralization.

(4)腐4ml質自身自メ然性があるため、脱水された
ケーキの焼却の際燃料費の大巾な削減(こなる。
(4) Since the 4ml cake itself is natural, fuel costs can be drastically reduced when incinerating the dehydrated cake.

(5)従米有機系高分子凝集剤のみを使用し真空脱水機
を使用して固欣分FgiLができ(ごくかったが、偶植
質と有機系高分子gE集剤を組合せれIJ゛貞空脱水機
を使用して固液分前か可能となる。
(5) A solid fraction FgiL was made using only a conventional organic polymer flocculant and a vacuum dehydrator (although it was very difficult to make, it was possible to make a solid fraction FgiL by combining an organic polymer flocculant with an organic polymer gE flocculant). It is possible to separate solids and liquids using an empty dehydrator.

以下、実施例により本発明をさらに説明するが本発明は
これに限定されるもので(」ない。
The present invention will be further explained below with reference to Examples, but the present invention is not limited thereto.

実施例1 下記の草炭おJ:び有機系高分子凝集剤を便用しこの脱
水剤を用いて、下記条件で有機性汚泥を脱水した。結果
を表−2に示す。
Example 1 Organic sludge was dehydrated using the following dehydrating agent and organic polymer flocculant under the following conditions. The results are shown in Table-2.

〔条件〕〔conditions〕

(1)有機性汚泥濃度は2.5% (2)各薬剤(草炭、有機系高分子凝集剤、その他の凝
集剤を指す)の添加量は対DS(汚泥固形分)θう (3)有機性汚泥の性質 生し尿士浄化槽汚泥 (4)脱水時の条件 ■真空圧:600薄WHgX10秒吸引 20秒脱水■
攪拌 : 200rpm X 1分 ■濾過面積:4T、8cノj ■P布 :サラン匝 90メツシュ 表−2
(1) Organic sludge concentration is 2.5% (2) Addition amount of each chemical (grass charcoal, organic polymer flocculant, and other flocculants) is relative to DS (sludge solid content) (3) Properties of organic sludge Raw septic tank sludge (4) Conditions for dehydration ■ Vacuum pressure: 600 thin WHg x 10 seconds suction, 20 seconds dehydration ■
Stirring: 200 rpm x 1 minute ■Filtration area: 4T, 8c noj ■P cloth: Saran trowel 90 mesh Table-2

Claims (1)

【特許請求の範囲】 1、質櫃貫および有機系高分子凝集剤を組合せてなる有
機性汚泥の固液分離性能のすぐれた脱水剤。 2、 腐碩質か草炭または/および草炭類似物質である
特許請求の範囲第1項化載の脱水剤。 3、 有機性汚泥に腐植質を一添加し、次いで有機系高
分子凝集剤を添卯し、l液分塵を行うことを特徴とする
脱水剤の使用法。
[Scope of Claims] 1. A dehydrating agent with excellent solid-liquid separation performance for organic sludge, which is formed by combining a solid sludge and an organic polymer flocculant. 2. The dehydrating agent according to claim 1, which is saprophyte, grass charcoal, or/and a grass charcoal-like substance. 3. A method for using a dehydrating agent, which comprises adding humus to organic sludge, then adding an organic polymer flocculant, and performing liquid separation.
JP56167679A 1981-10-19 1981-10-19 Dehydrating agent and using method Pending JPS5867399A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP56167679A JPS5867399A (en) 1981-10-19 1981-10-19 Dehydrating agent and using method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP56167679A JPS5867399A (en) 1981-10-19 1981-10-19 Dehydrating agent and using method

Publications (1)

Publication Number Publication Date
JPS5867399A true JPS5867399A (en) 1983-04-21

Family

ID=15854206

Family Applications (1)

Application Number Title Priority Date Filing Date
JP56167679A Pending JPS5867399A (en) 1981-10-19 1981-10-19 Dehydrating agent and using method

Country Status (1)

Country Link
JP (1) JPS5867399A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4552666A (en) * 1982-11-26 1985-11-12 Mueller Dietrich Process for the treatment of sewage sludge
WO1995019328A1 (en) * 1994-01-18 1995-07-20 Allplant Entwicklungs- Und Marketing Gmbh Cultivation substrate and process for producing it

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4552666A (en) * 1982-11-26 1985-11-12 Mueller Dietrich Process for the treatment of sewage sludge
WO1995019328A1 (en) * 1994-01-18 1995-07-20 Allplant Entwicklungs- Und Marketing Gmbh Cultivation substrate and process for producing it

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