JPS63141700A - Degradation treatment of oil-containing water sludge - Google Patents

Degradation treatment of oil-containing water sludge

Info

Publication number
JPS63141700A
JPS63141700A JP61289956A JP28995686A JPS63141700A JP S63141700 A JPS63141700 A JP S63141700A JP 61289956 A JP61289956 A JP 61289956A JP 28995686 A JP28995686 A JP 28995686A JP S63141700 A JPS63141700 A JP S63141700A
Authority
JP
Japan
Prior art keywords
sludge
oil
quicklime
water
moisture
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.)
Granted
Application number
JP61289956A
Other languages
Japanese (ja)
Other versions
JPH0442079B2 (en
Inventor
Masaaki Okuda
奥田 正昭
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 Petrochemical Co Ltd
Original Assignee
Sanyo Petrochemical 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 Sanyo Petrochemical Co Ltd filed Critical Sanyo Petrochemical Co Ltd
Priority to JP61289956A priority Critical patent/JPS63141700A/en
Publication of JPS63141700A publication Critical patent/JPS63141700A/en
Publication of JPH0442079B2 publication Critical patent/JPH0442079B2/ja
Granted legal-status Critical Current

Links

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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Landscapes

  • Treatment Of Sludge (AREA)
  • Solid Fuels And Fuel-Associated Substances (AREA)

Abstract

PURPOSE:To permit inexpensive and easy degradation of oil-contg. water sludge by adding granular quicklime and surfactant to the oil-contg. water sludge, kneading the sludge and subjecting the sludge to drying in the sun, thereby reducing and degrading the sludge. CONSTITUTION:The granular or lump quicklime, >=50wt.% of which consists of 1-20mm grain size, is added at 1-55wt.% and the surfactant (e.g., sodium alkylbenzene sulfonate) is added thereto at 0.1-10wt.% of the weight of the quicklime to the oil-contg. water sludge which is subjected to a pretreatment such as centrifugal sepn. at need or has <=90wt.% moisture by a distillation method equiv. to the moisture content of the sludge subjected to said treatment, then the sludge is kneaded and is treated without applying heat thereto from the outside. If necessary, the sludge is aged for 1-3 days and is dried in the sun, by which the moisture is evaporated and absorbed to reduce volume and the sludge is degraded. As a result, the treatment is realized at the low treat ment cost without entailing large equipment investment. The treated sludge having a high oil content is usable as solid fuel.

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は石油工場、油槽所、化学工場1発電所、船舶、
機械工場等から排出される含油水汚泥(含油、含水汚泥
)を粉化する処理方法に関するものである。
[Detailed Description of the Invention] [Industrial Application Field] The present invention is applicable to oil factories, oil depots, chemical factories, power plants, ships,
The present invention relates to a treatment method for pulverizing oil-containing water sludge (oil-containing, water-containing sludge) discharged from machine factories and the like.

[発明の背景コ 一般に含油水汚泥と称せられるものは、例えば長期にわ
たってM積された油槽の底部、あるいは工場のオイルセ
パレーターなどに蓄積されたものである。これらの含油
水汚泥は油分、水分のほか、泥分などの変質物、カーボ
ン、有機性不純物等を多量に含有し、見かけ粘度は増大
し、はとんどマヨネーズ状となって蓄積されている。
[Background of the Invention] What is generally referred to as oil-impregnated water sludge is, for example, accumulated over a long period of time at the bottom of an oil tank or in an oil separator in a factory. In addition to oil and water, these oily water sludges contain a large amount of altered substances such as mud, carbon, organic impurities, etc., and their apparent viscosity increases and is often accumulated in a mayonnaise-like state. .

従来はこれら含油水汚泥等の処理には焼却、活性汚泥法
、物理化学的方法の組み合わせ、界面活性剤の添加等、
一連の方法が提案されているが、最続的には焼却される
ものが多く(特開昭57−205491号参照)、焼却
費用が高価のためにその経済的負担は小さくない。
Conventionally, these oil-containing water sludges have been treated using methods such as incineration, activated sludge method, combination of physical and chemical methods, addition of surfactants, etc.
Although a series of methods have been proposed, many of the materials are ultimately incinerated (see Japanese Patent Laid-Open No. 57-205491), and the high cost of incineration poses a considerable economic burden.

また含油量の多い汚泥に対してはセメント等を用いて、
固形燃料として再利用することが提案されている(特公
昭57−43075号、同57−61075号、同58
−40998号、特開昭56−103296号、同57
−80493号、同57−190096号、同58−5
3989号参照)が、最近のような石油の値下がりの激
しい時代ては低エネルギー固形燃料の経済的価値は消失
し、この方法は現実的ではない。
In addition, for sludge with high oil content, use cement etc.
It has been proposed to reuse it as solid fuel (Special Publications No. 57-43075, No. 57-61075, No. 58).
-40998, JP-A-56-103296, JP-A-57
-80493, 57-190096, 58-5
(Refer to No. 3989) However, in the recent times when the price of oil is rapidly decreasing, the economic value of low-energy solid fuels disappears, and this method is not practical.

[発明の目的] 本発明はこのような時代に迅速に対応して為されたもの
であって、含油水汚泥の処理費を如何に低減できるかを
鋭意研究した結果、完成したものであフて、多大な設備
投資を伴わず、低コストの処理費用で実現可能なものと
して提案するものである。
[Purpose of the invention] The present invention was developed in response to these times, and was completed as a result of intensive research into how to reduce the processing cost of oil-containing water sludge. This is proposed as a method that can be realized at low processing costs without requiring large capital investments.

即ち、本発明は、含油水汚泥中の水分を蒸発、吸収して
減容するとともに油分を固定し1作業運搬時における取
扱を容易にし、また焼却の必要なものについては簡易な
焼却炉での焼却を可能にし、焼却を要しないものについ
ては埋立を容易に行うための含油水汚泥の処理法を提供
することをMSlの目的とし、油分の高いものについて
は固形燃料としても用いることもてき、また粉化に際し
ては高価な設備をも要しない極めて筒易な低コストの処
理法を提供することを第゛2の目的とする。
That is, the present invention evaporates and absorbs water in oil-containing water sludge to reduce its volume, fixes the oil content, and facilitates handling during transportation for one operation, and also allows materials that need to be incinerated to be burned in a simple incinerator. The purpose of MSl is to provide a treatment method for oil-containing water sludge that allows for incineration and facilitates landfilling of sludge that does not require incineration, and can also be used as solid fuel for sludge with a high oil content. The second object is to provide an extremely simple and low-cost processing method that does not require expensive equipment when pulverizing.

[発明の構成] 上記目的を達成するための本発明の含油水汚泥の粉化処
理法は、必要ならば遠心分離等の前処理を行い、または
この工程を経たのと同等の蒸留法による水分が90重量
%以下の含油水汚泥に対し、その50重量%以上が1〜
20mm径から成る粒状または塊状の生石灰1〜55重
量%(好ましくは5〜50重量%)と、生石灰に対し0
.1〜10重量%の界面活性剤を加え混練して外部から
熱を加えることなく処理し、必要なら1〜3日養生して
天日乾燥を行い、水分を蒸発、吸収して減容するととも
に粉化することを特徴とする。
[Structure of the Invention] In order to achieve the above object, the method for pulverizing oily water sludge of the present invention involves performing pretreatment such as centrifugation if necessary, or removing water by a distillation method equivalent to this process. is less than 90% by weight of oil-containing water sludge, and more than 50% by weight is 1-
1 to 55% by weight (preferably 5 to 50% by weight) of granular or lump quicklime with a diameter of 20 mm and 0% to quicklime.
.. 1 to 10% by weight of surfactant is added and kneaded, treated without applying external heat, and if necessary, cured for 1 to 3 days and dried in the sun to evaporate and absorb water to reduce volume. It is characterized by being powdered.

以下、本発明について詳述する。The present invention will be explained in detail below.

なお本発明に関する説明の中で使用する水分、泥分、油
分については混乱を避けるため次の測定法による値を使
用することとする。
In order to avoid confusion, the values of moisture, mud, and oil used in the description of the present invention will be based on the following measurement method.

水分: JIS K 2275 (蒸留法)油分: J
IS K 0120 (ノルマルヘキサン抽出法)泥分
:泥分=1−木分−油分 %:重量% 本発明は含油水汚泥のうち、水分が90%以下の汚泥を
対象とするもので、水分が90%を超えるものについて
は使用する生石灰が多量となり経済的てない、しかし水
分が90%を超えるものについては前処理を行うことに
よって容易に水分を減少せしめることが可能である。
Moisture: JIS K 2275 (distillation method) Oil content: J
IS K 0120 (Normal hexane extraction method) Sludge content: Sludge content = 1 - Wood content - Oil content %: Weight % This invention targets sludge with a water content of 90% or less among oil-containing water sludges. If the moisture content exceeds 90%, a large amount of quicklime will be used, making it uneconomical.However, if the moisture content exceeds 90%, it is possible to easily reduce the moisture content by performing pretreatment.

本発明を適用する含油水汚泥とは、石油工場、油槽所、
化学工場1発電所、船舶1機械工場等から排出されるも
のて、遠心脱水機、フィルタープレス等の機械的処理に
て容易に多量水分を除去したもの、濃縮沈降槽で沈降堆
積した汚泥または浮上汚泥および油タンク等で長期にわ
たって堆積したもの等である。これらの含油水汚泥は通
常含水率90%以下、含油率50%以上で半流動性、グ
リース状またはペースト状を呈し現行法規では埋立処分
不可能とされ、焼却処分としてしか処分できないもので
ある。
Oil-containing water sludge to which the present invention is applied refers to oil factories, oil depots,
Materials discharged from chemical plants (1) power plants, ships (1) machinery factories, etc., from which a large amount of moisture has been easily removed through mechanical processing such as centrifugal dehydrators and filter presses, and sludge that has settled and accumulated in thickening sedimentation tanks or floats. These include sludge and things that have accumulated over a long period of time in oil tanks, etc. These oil-impregnated water sludges usually have a water content of 90% or less and an oil content of 50% or more and are semi-fluid, grease-like or paste-like, and cannot be disposed of in a landfill under current regulations, and can only be disposed of by incineration.

本発明は粉化処理剤として生石灰を用いるものであるが
、少なくとも50%が1〜20■l径である粒状乃至塊
状の生石灰を用いるものである。尚ここで「径」とは球
状体である場合はその直径をいい1球状体以外の形状の
場合は同体積に換算したときの球状体の直径をいう。
The present invention uses quicklime as a powdering agent, and uses quicklime in the form of granules or lumps, at least 50% of which has a diameter of 1 to 20 liters. Note that the term "diameter" herein refers to the diameter of a spherical body, and in the case of a shape other than a spherical body, the term "diameter" refers to the diameter of the spherical body when converted to the same volume.

従来含油汚泥、含油スラッジからの固形燃料を生石灰単
独、生石灰と他の薬剤と混合して用いる提案がなされて
いるが5本提案の如き生石灰の粒径に言及したものは見
当たらない。
Conventionally, proposals have been made to use oil-impregnated sludge or solid fuel from oil-impregnated sludge as quicklime alone or as a mixture of quicklime and other chemicals, but there is no mention of the particle size of quicklime as in the five proposals.

生石灰は空気中に放置すれば水を吸収して発熱を伴いな
がら消石灰に変化するのは公知であるが、前述の提案は
いずれもこの事実に注意を払っていない、生石灰を工業
的に用いるに際し、最も注意しなけらばならないのは、
貯蔵中における水の吸収による変質である。包装の不適
切、貯蔵期間の増大等によって生石灰が消石灰に変質し
たとすれば、本処理法の効果が激減し、処理に必要な生
石灰量は増大し、直接的な処理費用の増大をもたらすの
みならず、粉化処理後の処理費の増大をも招来するもの
である。また粉状生石灰の添加作業、混練作業において
飛散することは作業従事者に対して大きな危険をもたら
すものであり、これもまた大きなマイナス要因となり得
る。このため種々検討の結果、少なくとも50%が1〜
20m■径の粒状もしくは塊状である生石灰を用いるこ
とが、貯蔵時の変質を防止し、作業時の安全性を高める
ことを見出したものである。
It is well known that when quicklime is left in the air, it absorbs water and turns into slaked lime with heat generation, but none of the above proposals pay attention to this fact. , the most important thing to be careful of is
This is a change in quality due to water absorption during storage. If quicklime were to change into slaked lime due to improper packaging or an extended storage period, the effectiveness of this treatment method would be drastically reduced, the amount of quicklime required for treatment would increase, and this would only lead to a direct increase in treatment costs. This also results in an increase in processing costs after the powdering process. In addition, scattering during the addition and kneading operations of powdered quicklime poses a great danger to workers, and this can also be a major negative factor. For this reason, as a result of various studies, at least 50% of
It has been discovered that using quicklime in the form of granules or lumps with a diameter of 20 m can prevent deterioration during storage and improve safety during work.

[発明の作用] 本発明における生石灰の作用効果は含油水汚泥中の水分
との反応による発熱による水分の蒸発、生石灰と水の反
応による消石灰の生成、消石灰の水分、油分の吸収等に
よる減容、粉化作用であるが、生石灰が粒状、塊状の場
合は表面積が小さいための反応速度の減退、反応に要す
る時間の増大が懸念されるところであるが、この懸念は
界面活性剤の併用によって取り除かれることが判明し。
[Action of the invention] The effects of quicklime in the present invention include evaporation of water due to heat generated by reaction with water in oil-containing water sludge, generation of slaked lime by the reaction between quicklime and water, and volume reduction due to absorption of water and oil in slaked lime. Regarding the pulverization effect, if quicklime is in the form of granules or lumps, there are concerns that the reaction rate will decrease and the time required for the reaction will increase due to the small surface area, but this concern can be alleviated by using a surfactant in combination. It turns out that it will happen.

これによって本発明を完成するに至ったものである。This led to the completion of the present invention.

生石灰と同時に界面活性剤゛を添加すると、界面活性剤
によって含有する水の表面張力が低下し、粒状、塊状の
生石灰の中に水が容易に浸透し発熱にともなって、粒状
、塊状の生石灰は粉状に破砕され反応は容易に進行する
ものである。
When a surfactant is added at the same time as quicklime, the surfactant lowers the surface tension of the water contained in it, allowing water to easily penetrate into the granular and lumpy quicklime and generate heat, causing the granular and lumpy quicklime to It is crushed into powder and the reaction proceeds easily.

本発明における界面活性剤の添加量としては添加する生
石灰に対して0.1〜10%添加されるが、0.1〜1
%が好ましい範囲である。0.1%未満ては上記本発明
の効果が得られにくく、逆に10%を越える量では効果
が飽和してコスト的にマイナスである。また界面活性剤
の種類としては、陰イオン界面活性剤1wAイオン界面
活性剤、非イオン界面活性剤のどれでもよいが、陰イオ
ン界面活性剤が適しており、アルキルベンゼンスルホン
酸ソーダ、アルキル硫酸エステルソーダ塩、アルキル硫
酸ソーダ等が特に適している。
The amount of surfactant added in the present invention is 0.1 to 10% based on the added quicklime, but 0.1 to 1%.
% is a preferred range. If the amount is less than 0.1%, it is difficult to obtain the above-mentioned effects of the present invention, whereas if the amount exceeds 10%, the effect is saturated and the cost is negative. The type of surfactant may be either an anionic surfactant, 1wA ionic surfactant, or nonionic surfactant, but anionic surfactants are suitable, such as sodium alkylbenzene sulfonate, sodium alkyl sulfate ester, etc. Particularly suitable are salts, alkyl sodium sulfates, and the like.

これらの界面活性剤は塊状のものは混線時、生石灰の添
加前に含油水汚泥に添加する方が好ましく、粉状の界面
活性剤を使用する場合は、生石灰と同時に添加すること
が望ましい。
When these surfactants are in bulk form, it is preferable to add them to the oil-impregnated water sludge before addition of quicklime at the time of mixing, and when using powdered surfactants, it is desirable to add them at the same time as quicklime.

生石灰の添加量は含有水分の量に応均て変化させること
が望ましく、水分の多い場合は添加量が多く、水分が少
ない場合はそれに応じて生石灰の添加量を減することが
経済的である。また生石灰の添加量を高めれば処理時間
、養生時間は短縮可能であるが、処理費用が増大するか
ら、状況に応じて生石灰の量を適切に保持することが必
要である。
It is desirable to change the amount of quicklime added depending on the amount of moisture content; it is economical to increase the amount added when the moisture content is high, and reduce the amount added accordingly when the moisture content is low. . Further, if the amount of quicklime added is increased, the processing time and curing time can be shortened, but the processing cost increases, so it is necessary to maintain the amount of quicklime appropriately depending on the situation.

本発明における養生日数としては3日を超えると粉化状
況が改善される度合が少なくなるから。
In the present invention, if the curing period exceeds 3 days, the degree of improvement in the powdering condition will be reduced.

3日以内とすることが経済的に望ましい養生期間である
An economically desirable curing period is 3 days or less.

混練作業にあたっては本発明の場合は高価な設備は必ず
しも必要でなく、容量が少ない場合は混合槽で手作業で
も十分可能であり、コンクリートミキサー車を使用する
ことも可能である。また連続自動装置を用いることも可
能であり、処理量に応じて適切な設備を考えればよい。
In the case of the present invention, the kneading work does not necessarily require expensive equipment, and if the capacity is small, it is sufficient to perform the kneading work manually in a mixing tank, or it is also possible to use a concrete mixer truck. It is also possible to use a continuous automatic device, and it is only necessary to consider appropriate equipment depending on the throughput.

[実施例] 以下実施例によって本発明を説明する。尚、以下「部」
とは「重量部」を表わす。
[Example] The present invention will be explained below with reference to Examples. In addition, hereinafter referred to as “Department”
means "parts by weight".

実施例 l 試 料 製油所から排出された含油水汚泥性状 ■外観 黒褐色、不透明、泥状 ■水分 80.7% ■泥分 11.1% ■油分 8.2% 上記含油水汚泥試料100部に対し、生石灰(90%が
1〜20sn径からなる粒状体)30部及びドデシルベ
ンゼンスルホン醜ソーダ1部を加えたのち30分間混練
した後、2日間放置し天日養生を行った。
Example l Sample Properties of oil-impregnated water sludge discharged from an oil refinery ■ Appearance Dark brown, opaque, muddy ■ Moisture 80.7% ■ Sludge content 11.1% ■ Oil content 8.2% To 100 parts of the above oil-impregnated water sludge sample To the mixture, 30 parts of quicklime (90% of granules having a diameter of 1 to 20 sn) and 1 part of dodecylbenzenesulfone soda were added and kneaded for 30 minutes, then left to stand for 2 days and cured in the sun.

含油水汚泥は粉化し、極めて取扱い容易なものに変化し
た。混練時には外部より加熱する必要は無く、反応熱の
ため汚泥の温度は最高125℃に達し、水分の蒸発がl
l1I測された。2日間の天日養生後、全重量は照合油
水汚泥に対し、はとんど増大しない。
The oil-impregnated water sludge was pulverized and transformed into something that was extremely easy to handle. There is no need for external heating during kneading, and the temperature of the sludge reaches a maximum of 125°C due to the heat of reaction, reducing water evaporation.
l1I was measured. After 2 days of solar curing, the total weight hardly increases compared to the control oil-water sludge.

比較例 1 実施例1と同一の含油水汚泥、同じ生石灰を同量用いた
が、ドデシルベンゼンスルホン酸ソーダを添加しなかっ
た。実施例1と同様に混練した後、同様に2日間の天日
養生を行った。
Comparative Example 1 The same oil-impregnated water sludge and the same amount of quicklime as in Example 1 were used, but sodium dodecylbenzenesulfonate was not added. After kneading in the same manner as in Example 1, the mixture was similarly cured in the sun for 2 days.

混練時の最高温度は110℃にとどまり、2日後の全重
量は照合油水汚泥よりも全重量として10%程多かった
。粉化した汚泥中には白色の生石灰が未反応のまま塊状
に残存していることが認められた。
The maximum temperature during kneading remained at 110°C, and the total weight after 2 days was about 10% higher than the reference oil-water sludge. It was observed that unreacted white quicklime remained in the powdered sludge in the form of lumps.

比較例 2 実施例1と同じ含油水汚泥に対し、購入後湿度60%て
3週間貯蔵した粉状生石灰(11鳳径未満のものが70
%以上)を用い、実施例1と同様な実験を行ったが、混
練時の最高温度は105℃にとどまり、2日間養生後の
全重量は15%増大した。原料生石灰が貯蔵中に水を吸
収して変質していたものと思われる。
Comparative Example 2 The same oil-impregnated water sludge as in Example 1 was treated with powdered quicklime that had been stored for 3 weeks at a humidity of 60% after purchase (those with a diameter of less than 11% had a diameter of 70%).
% or more), the same experiment as in Example 1 was conducted, but the maximum temperature during kneading remained at 105° C., and the total weight after curing for 2 days increased by 15%. It is thought that the raw material quicklime absorbed water and deteriorated during storage.

実施例 2 実施例1において試料台油水汚泥(水分92%、泥分6
%、油分2%)のものを用いたことのみ異ならせて同様
の実験を行ったが、水分が多く粉化することができなか
った。
Example 2 In Example 1, the sample table oil-water sludge (moisture 92%, mud content 6
%, oil content: 2%), but the water content was too high and it could not be powdered.

この試料を遠心分g1機(3000rpm)にかけて水
分を60%除去させて実施例1と同様の実験を行ったと
ころ、粉化処理が可能となり、全重量は約5%減量した
When this sample was centrifuged in a G1 machine (3000 rpm) to remove 60% of water and an experiment similar to Example 1 was carried out, powdering treatment became possible and the total weight was reduced by about 5%.

実施例 3 実施例1においてドデシルベンゼンスルホン酸ソーダに
代えてナトリウムジアルキルスルホサクシネート0.5
部を用いたことのみ異ならせ、同様の実験を行ったとこ
ろ、反応時間20分間て反応が完了した。3日間の天日
養生後、全重量は5%減少した。
Example 3 In Example 1, sodium dialkylsulfosuccinate 0.5 was substituted for sodium dodecylbenzenesulfonate.
When a similar experiment was carried out with the only difference that 100% of the sample was used, the reaction was completed in 20 minutes. After 3 days of sun curing, the total weight decreased by 5%.

実施例 4 試 料 タンク底油 性状 ■外観 黒褐色、マヨネーズ状 ■水分 45% ■泥分 18% ■油分 37% 上記含油水汚泥試料100部に対し、生石灰(70%が
1〜10■■径からなる粒状体)15部及びセチル硫酸
エステルソーダ塩1部を加え、30分間混練して粉化し
た。1日間の天日養生を行ったところ、全重量は照合油
水汚泥とほぼ同じであった。
Example 4 Sample Tank bottom oil property ■ Appearance blackish brown, mayonnaise-like ■ Moisture 45% ■ Sludge content 18% ■ Oil content 37% Quicklime (70% is from 1 to 10 mm diameter) 15 parts of granular material) and 1 part of cetyl sulfate sodium salt were added and kneaded for 30 minutes to powder. After curing in the sun for one day, the total weight was almost the same as the reference oil-water sludge.

Claims (1)

【特許請求の範囲】[Claims] 必要ならば遠心分離等の前処理を行い、またはこの工程
を経たのと同等の蒸留法による水分が90重量%以下の
含油水汚泥に対し、その50重量%以上が1〜20mm
径から成る粒状または塊状の生石灰1〜55重量%と、
生石灰に対し0.1〜10重量%の界面活性剤を加え混
練して外部から熱を加えることなく処理し、必要なら1
〜3日養生して天日乾燥を行い、水分を蒸発、吸収して
減容するとともに粉化することを特徴とする含油水汚泥
の粉化処理法。
If necessary, perform pretreatment such as centrifugation, or use a distillation method equivalent to that which has gone through this process to obtain oil-containing water sludge with a water content of 90% by weight or less, where 50% by weight or more is 1 to 20 mm.
1 to 55% by weight of granular or lump quicklime consisting of a diameter,
Add 0.1 to 10% by weight of a surfactant to quicklime, knead it, and process without applying external heat.
A method for pulverizing oil-impregnated water sludge, which is characterized by curing for ~3 days, drying in the sun, evaporating and absorbing water to reduce the volume, and pulverizing the sludge.
JP61289956A 1986-12-04 1986-12-04 Degradation treatment of oil-containing water sludge Granted JPS63141700A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61289956A JPS63141700A (en) 1986-12-04 1986-12-04 Degradation treatment of oil-containing water sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61289956A JPS63141700A (en) 1986-12-04 1986-12-04 Degradation treatment of oil-containing water sludge

Publications (2)

Publication Number Publication Date
JPS63141700A true JPS63141700A (en) 1988-06-14
JPH0442079B2 JPH0442079B2 (en) 1992-07-10

Family

ID=17749910

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61289956A Granted JPS63141700A (en) 1986-12-04 1986-12-04 Degradation treatment of oil-containing water sludge

Country Status (1)

Country Link
JP (1) JPS63141700A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2004026773A1 (en) * 2002-08-13 2004-04-01 Korea Institute Of Science And Technology Method for advanced wastewater treatment without excess sludge using sludge disintegration

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2004026773A1 (en) * 2002-08-13 2004-04-01 Korea Institute Of Science And Technology Method for advanced wastewater treatment without excess sludge using sludge disintegration

Also Published As

Publication number Publication date
JPH0442079B2 (en) 1992-07-10

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