JPS59105809A - Concentration of liquid by membrane - Google Patents

Concentration of liquid by membrane

Info

Publication number
JPS59105809A
JPS59105809A JP21659482A JP21659482A JPS59105809A JP S59105809 A JPS59105809 A JP S59105809A JP 21659482 A JP21659482 A JP 21659482A JP 21659482 A JP21659482 A JP 21659482A JP S59105809 A JPS59105809 A JP S59105809A
Authority
JP
Japan
Prior art keywords
membrane
liquid
substance
colloidal
amount
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
JP21659482A
Other languages
Japanese (ja)
Inventor
Yasuo Miyata
宮田 康夫
Tsuneo Abe
恒夫 阿部
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.)
IHI Corp
Original Assignee
IHI 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 IHI Corp filed Critical IHI Corp
Priority to JP21659482A priority Critical patent/JPS59105809A/en
Publication of JPS59105809A publication Critical patent/JPS59105809A/en
Pending legal-status Critical Current

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  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

PURPOSE:To prevent the adhesion of suspended substance or colloidal substance to a membrane surface to hold the amount of water to be permeated through the membrane to a good state, by converting the suspended substance or the colloidal substance in a liquid to a flocculated aggregate while controlling the pH of the membrane side residual liquid to a specific range. CONSTITUTION:When aluminum sulfate is added to the washing waste liquid with TDS of 400-6,000ppm containing suspended substance and colloidal substance in a raw water tank 2 in an amount of 150-170ppm as a flocculant while the pH of said waste liquid is adjusted to 5.3-5.7 by sulfuric acid. The waste liquid is raised in pressure to 40kg/cm<2> by a pressure pump 3 and passed through a cellulose acetate membrane 5 with a NaCl removal ratio of about 90% to be separated into a membrane permeate 6 and a membrane side residual liquid 7 while this residual liquid 7 is concentrated to 1/20-1/40 in a volume ratio. By this method, the suspended substance and the colloidal substance are subjected to the neutralization and coarse pulverization of the surface potential due to the addition of coagulant and pH adjustment and thereby the affinity with the membrane is lost.

Description

【発明の詳細な説明】 本発明は膜に付着しやすい懸濁物貢及びコロイド状物質
を含む、夜の膜透過水量を良好な状態に保持し、核酸の
濃縮をOT能ならしめる模による液体濃縮方法に関する
DETAILED DESCRIPTION OF THE INVENTION The present invention provides a method to maintain the amount of water permeated through the membrane during the night, including suspended particles and colloidal substances that tend to adhere to the membrane, and to make the concentration of nucleic acids an OT function. Regarding the concentration method.

一般に、膜分離方法によって、有機系又は無機系物質を
含む液を処理する@、懸濁物質及びコロイド状物質が膜
面に付着し、そのために、膜透過液量を著しく低下させ
ることがある。その対策として、被処理液の前処理とし
て、膜面に付着しやすい物質を除去することが行なわれ
て−る。たとえば、凝集沈殿、砂f過、遠心分離、活性
炭吸着処理などを単独、あるいは組合わせた前処理″が
行なわれている。しかし、これらの方法は処理システム
を複雑にするばかりでなく、設備費、ランニングコスト
を大幅に上昇させるとhう欠点がある。
Generally, when membrane separation methods are used to process liquids containing organic or inorganic substances, suspended solids and colloidal substances adhere to the membrane surface, which can significantly reduce the amount of liquid that permeates through the membrane. As a countermeasure against this problem, pretreatment of the liquid to be treated is performed to remove substances that tend to adhere to the membrane surface. For example, pretreatment methods such as coagulation-sedimentation, sand filtration, centrifugation, and activated carbon adsorption treatment are carried out singly or in combination. However, these methods not only complicate the treatment system but also increase equipment costs. However, it has the disadvantage of significantly increasing running costs.

本発明は上記の従来法の欠点を解決し、lft!濁物質
及びコロイド状物質を含む液の膜透過処理システムの(
副易化をOT能ならしめる膜による液体濃縮法を提供す
るもので、その要旨とするところは、懸濁物機およびコ
ロイド状物質を含む液体を膜分離で濃縮処理をするに当
り、該液体に凝集剤を添加して該懸濁物質およびコロイ
ド状物質を凝集集合体とするとともに#Ii¥側残留液
のpHを5.3〜5.7の範囲にコントロールし、膜透
過水量を所定レベルに保持することを特徴と量る膜によ
る液体濃縮法、にある。
The present invention solves the above-mentioned drawbacks of the conventional method and provides lft! Membrane permeation treatment system for liquids containing turbid substances and colloidal substances (
The present invention provides a method for concentrating liquids using membranes that enables OT functionality for subdivision. A flocculant is added to make the suspended matter and colloidal matter into agglomerated aggregates, and the pH of the #Ii\ side residual liquid is controlled within the range of 5.3 to 5.7, and the amount of water permeated through the membrane is maintained at a predetermined level. There is a method of liquid concentration using a weighing membrane, which is characterized by the retention of

次に、本発明を図面によって説明する。Next, the present invention will be explained with reference to the drawings.

第1図は本発明の1実施例のフローシート図、第2図は
セルローズアセテート膜透過水量の経時変化を示すグラ
フ図、第3図は容積化で1/2oに減容した時の膜透過
水数の経時変化を示すグラフ図である。
Fig. 1 is a flow sheet diagram of one embodiment of the present invention, Fig. 2 is a graph showing changes in the amount of water permeated through a cellulose acetate membrane over time, and Fig. 3 is a permeation through the membrane when the volume is reduced to 1/2O It is a graph diagram showing a change in the number of water over time.

すなわち、本発明は被処理液に、被処理液中の懸濁物質
及びコロイド状物質を凝集させる凝集剤を添加し、かつ
該凝集剤が効果的に凝集複合物を作るに必要なPH範囲
とするために、酸又はアルカリ液を添加した後、膜分離
装置zで処理するとともに、処理中はpH範囲を一定の
範囲内にコントロールするものである。凝集剤としては
Fe、Atなとの水酸化物または塩類が有効であり、酸
としては塩酸、硫酸などが、またアルカリとしては力性
ソーダ7よとが用すられる。
That is, the present invention adds a flocculant to the liquid to be treated to flocculate suspended matter and colloidal substances in the liquid to be treated, and adjusts the pH range necessary for the flocculant to effectively form a flocculated composite. In order to do this, after adding an acid or alkaline solution, it is treated with a membrane separator z, and the pH range is controlled within a certain range during the treatment. As the flocculant, hydroxides or salts of Fe, At, etc. are effective, as the acid, hydrochloric acid, sulfuric acid, etc., and as the alkali, sodium hydroxide is used.

本発明方法により、膜に付着し易い懸濁物質及びコロイ
ド状物質は添加されたa築刑と適当なp HLEA j
Mとによって、#集集合体となり、その衣面電位の中和
、粒子の粗大化などが起こり、使用される膜材質との関
係において、膜との親和性を失い、膜に付着しにくい性
状のものとなる。これにより、被処理液を、襖分離処理
するに際し、清縮ノ(の向上に伴う繞透過液量の低下を
大幅に防止することができる。
According to the method of the present invention, suspended solids and colloidal substances that tend to adhere to the membrane are added to the membrane at a suitable pH level.
M forms an aggregate, which causes neutralization of the surface potential and coarsening of the particles, which causes them to lose affinity with the membrane and become difficult to adhere to the membrane due to the relationship with the membrane material used. Becomes the property of Thereby, when subjecting the liquid to be treated to the sliding door separation treatment, it is possible to significantly prevent a decrease in the amount of liquid passing through the canal due to an improvement in the cleaning ratio.

また、本発明方法において使用する峡としては、中空I
J4、平板映、゛に状膜、のり巻き両膜のものが利用で
きる。模1オ質としてはセルローズアセテート糸やポリ
アミド、ポリエステル、ポリアクリルニトリル、ポリス
ルホン糸の材料を丈)Iルた有礪糸枳、あるLnJ−j
金属水貨化物などの無機系編が使711できる。シ違換
分端の作用圧は約0.2 ttいし” ” ’/Cm’
 、好ましくは5〜55 ”J’ f乙、2である。
Further, as the isthmus used in the method of the present invention, hollow I
J4, flat film, ni-shaped film, and glue-wound film types are available. Materials used include cellulose acetate yarn, polyamide, polyester, polyacrylonitrile, and polysulfone yarn.
Inorganic materials such as metal water cargoes can be used. The working pressure at the switching end is approximately 0.2 tt/Cm.
, preferably 5 to 55 "J' f Otsu, 2.

第1図の不発明の1実線例のフローシート図において、
原水タンク2P’SのpH7,3,砥導膚50υ〜70
0μv/。、TDI!1400〜600 pplnの懸
濁物′Mおよびコロイド状物質をよむ洗Wl廃液を加圧
ポンプ3で””’/’m’に昇圧し、NAC1lrk’
lE4約90%のセルローズアセテート族5で原水温度
20〜30°Cにてm透禰水6と狭測残貿液7(一般に
磯縮液と込う)K−分離し、ノ4鵠透d水6を系外に・
11!り出すことにより、構1111I残貿液を容積化
で’20〜1/4oに、或容−縮するため1%分、1け
ft9ものである。
In the flow sheet diagram of one solid line example of non-invention in FIG.
Raw water tank 2P'S pH 7.3, abrasive conductor 50υ~70
0 μv/. , TDI! The washing Wl waste liquid containing 1,400 to 600 ppln of suspension 'M' and colloidal substances was pressurized to '''/'m' with pressure pump 3, and NAC1lrk'
1E4 Approximately 90% cellulose acetate group 5 is separated at a raw water temperature of 20 to 30°C from 100% water 6 and 30% liquid 7 (generally included as condensate), and 4) Water 6 out of the system.
11! By taking out the remaining liquid from the structure, the volume is reduced to 20 to 1/4 o, which is 1%, or 1 ft9.

次に、%)A′F491Iによって本暢明tさらに具体
的に説明する。
Next, this will be explained in more detail using %) A'F491I.

42図はI凄果剤を使用しlzr場けで、この4廿は原
水のpilを使t(iするセル日−ズアセテートー〇m
*ザ屏速皮の最も小さいPH5゜5に濾Cよ(10十1
)を用りて、、4vIL比後、セルローズアセテート映
を装増し次セルに通液した4片のu4透過水饋の゛j峙
炭化はm2図にホtごとくで、hった。す7【わら、機
透過水量は90分後には処理1η後の1/2とへ激に低
ドした。
Figure 42 shows the IZR scene using the I-acid medicine.
*Filter C to the lowest pH of the folding skin, 5°5 (1011
), after the 4v IL ratio, the four pieces of U4 permeated water which were added to the cellulose acetate film and passed through the next cell were carbonized as shown in the m2 diagram. 7. After 90 minutes, the amount of water permeated through the machine was reduced to 1/2 after 1η of treatment.

これに対し、本発明方法では原水タン゛り2内のノ徂水
に対し、ml病としてs ft1tr貸アルミニウム(
A4 CC804) ・14〜181110)を150
〜1701)2m添加するとともに1遣終p H1に5
.3〜5.7のψα頭に(r4t4 C10+1 )に
よりtA 壕L fc (’) チ、a rci L、
 テtA容1府けるとともに、滅容副縮に伴べ上昇する
4 t’?I aのpHを(+tV(10+1 )K!
すPH5,3〜5.7の軸回にコントロールすると、第
3図に示すごとき曲Nが得られる。
On the other hand, in the method of the present invention, for the water outside the raw water tank 2, sft1tr aluminum (
A4 CC804) ・14-181110) 150
~1701) Add 2m and increase the final pH of 5 to 1
.. At the ψα head of 3 to 5.7 (r4t4 C10+1), tA trench L fc (') chi, a rci L,
4 t' ? The pH of Ia is (+tV(10+1)K!
When the PH value is controlled to be 5.3 to 5.7, a song N as shown in FIG. 3 is obtained.

43図は凝集111を使用する本発明方法の一合で谷1
纜比で1/20に減容した時の膜透過水量の経時変化を
示すもので、峻初原水タンク2に用意した原水が少ない
ため、別に用意したタンクにおいて、IJIl を七A
巣刊の岳加と前記硫酸くより前記pH4+i囲にhti
 qi したものを原水タンク2に適時追加する方法を
とった。最#1時には5uetの原水’140tに、ル
1するとともに、7601の膜−AJ4水を潜た。
Figure 43 shows valley 1 in one set of the inventive method using agglomeration 111.
This shows the change over time in the amount of water that permeates through the membrane when the volume is reduced to 1/20 in terms of actual volume.Since there is not enough raw water in the steep raw water tank 2, IJIl was added to 7A in a separate tank.
Takeka and the sulfuric acid in the magazine, the pH 4+i, and the hti
We adopted a method of adding qi to raw water tank 2 at the appropriate time. At the latest #1, I submerged 7601 membrane-AJ4 water in 5 uet of raw water '140t and at the same time.

+!!4aa /に墳の種峙的低ドは大向−に改筈され
、14゜以上の減容−線処理が効率良〈実施できること
が認めら九fc0 哨1表はこの場合の原水、襖透過水、Cむ6水の水道値
をポしたもので、効4良く・メ+罐さtしていることが
わかる。
+! ! In 4aa/, the depth of the burial mound was changed to Ōmukai, and it was recognized that a volume reduction of 14 degrees or more could be carried out efficiently. This is a combination of the water values for water and C6 water, and it can be seen that the effect is 4 good.

上11山威容闘縮過慢の#I傾液のpHは経時的に上昇
するが、これをそのまま放置し、pH6以上にすると、
模透過水墳の嘘ドが顕著に起こり、その11 P Hを
5.3〜5.717)範1cJijしてt、i、ai水
Ikの回復は認められlよかった。従って、減容11惰
僅梶のpHコントロールも非常に重要な要素である。
The pH of the #I tilted liquid of the top 11 mountains will rise over time, but if you leave it as it is and the pH reaches 6 or higher,
It was good to see that the 11 PH of the pseudo-permeable water mound was in the range of 5.3 to 5.717) and the recovery of t, i, ai water Ik was observed. Therefore, pH control is also a very important factor.

lよお、凝集剤のJ陵はim単lよビーカ試醜により1
、礎暎剤の曖i6よび凝集剤添JJu堤のt夜pHを変
化させ、それぞれの東洋Fでcrd襖フロックの生成具
合を目視によりd祭し、Jt終的にで礎過フロックが十
分に生成し、かつ最終pHが使用する旗の最適使用pH
値5,5付近とt’lるようt4果剤量として求めるこ
とができシ、。また、pkIコントロール範囲の上限は
#llラフロック十分に生成する最終PHの値から、ま
たド限は使用する酸の欲が過大にならないf4囲として
求められる。
1, the flocculant is 1 by the beaker test.
, by changing the pH of the JJu embankment with the foundation adhesion agent and flocculant added, and visually observing the formation of crd fusuma flocs in each Toyo F, it was determined that the foundation flocs were sufficiently formed in the Jt final stage. Optimum pH for use of flags produced and final pH used
It is possible to determine the amount of fruit juice at t4 so that the value is around 5.5. Further, the upper limit of the pkI control range is determined from the final pH value at which #ll rough floc is sufficiently generated, and the upper limit is determined as the f4 range in which the acidity used does not become excessive.

このように、本@明方法では被処理tfi ICtp集
剤を添加し、かつその凝集剤が良好lよ4楽効果を示す
pH1c/li時コントロールさせ、かつcm凝集剤適
汝およびpH条件はill 41 rjヒビ−−ワーク
で求めることができる。
As described above, in this @mei method, the TFI ICtp flocculant to be treated is added, and the pH is controlled at 1c/li when the flocculant exhibits a good effect, and the appropriateness of the cm flocculant and the pH conditions are 41 rj crack-work.

第1表 ()内はpHtA優、凝嗅刑添圓後の値をボす。Table 1 Values in parentheses indicate pHtA values after concentration and odor control.

木厖明の効果は次の1座りである。The effect of Mokukumei is the following 1 sitting.

11)  謹雑な前処理工程を44しても、棋分離にお
ける編層への一一物實及びコロイド伏吻嵐の付涜を防止
でき、換分虐処理の効ぷを向上させることがCぎる。
11) Even if a complicated pre-treatment process is performed, it is possible to prevent the damage to the formation layer during shogi separation and to prevent the addition of colloidal abrasions, and to improve the effectiveness of the conversion process. Giru.

(2)  前処理工程の省略により、設備費の低7或が
期待Cきる。
(2) By omitting the pretreatment process, equipment costs can be expected to be lower.

+3)嘱面への(様陶a貞及びコロイド状物繊付宥を防
止できるので、膜の洗#頻度を大−に減少させることが
できる。
+3) Since it is possible to prevent the adhesion of particles and colloidal materials to the membrane surface, the frequency of cleaning the membrane can be greatly reduced.

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

#&1図は本発明の1実施例のフローシート図、IJc
2図は凝集剤を使用しないjik合のセル四−ズアセf
−4・・4透噛水凌の経4f化をボナグラフ図、通3図
は不発明の凝・6刊を使用し、かつ1ダ積比で1/20
に61.容し1c時の11祷透輸7大曖の経時変化を2
バすグラフ図である。 図において、 l・・・・攪 拌 磯   50・・セルローズアセテ
ート幌200涼水タンク   6・−・・排出する祠選
14水3−・・・lJu圧ボング  7・・・・Ht4
適11  水4・・Φ・I拠Q1過水タンク
# & 1 Figure is a flow sheet diagram of one embodiment of the present invention, IJc
Figure 2 shows cell four-seed f without using a flocculant.
-4...4 Bonagraph diagram of the 4f version of Suiryo Toukami, 3rd diagram uses the 6th issue of the uninvented book, and the 1 da area ratio is 1/20
61. Changes over time of 11 prayers and 7 great ambiences at the time of 1c
FIG. In the figure, l... Stirring rock 50... Cellulose acetate canopy 200 Cool water tank 6... Draining shrine selection 14 Water 3-... l Ju pressure bong 7... Ht4
Suitable 11 Water 4...Φ・I base Q1 overwater tank

Claims (1)

【特許請求の範囲】[Claims] +1)  JIilG濁物貞およびコロイド状物質を含
む液体を膜分離で濃縮処理をするに当り、該液体に1芙
集剤を添加して該懸濁物質およびコロイド状物質を凝集
集合体とするとともに腹側残留液のpHを5.3〜5,
7の範囲にコントロールし、膜透過水量を所定レプルに
保持することを特徴とする膜に、よる液1イ;濃m法。
+1) When concentrating a liquid containing JIILG suspended matter and colloidal substances by membrane separation, an aggregating agent is added to the liquid to turn the suspended substances and colloidal substances into aggregates. Adjust the pH of the ventral residual fluid to 5.3 to 5.
Solution 1a: Concentration method using a membrane, which is controlled within the range of 7 and maintains the amount of water permeated through the membrane at a predetermined level.
JP21659482A 1982-12-10 1982-12-10 Concentration of liquid by membrane Pending JPS59105809A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP21659482A JPS59105809A (en) 1982-12-10 1982-12-10 Concentration of liquid by membrane

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP21659482A JPS59105809A (en) 1982-12-10 1982-12-10 Concentration of liquid by membrane

Publications (1)

Publication Number Publication Date
JPS59105809A true JPS59105809A (en) 1984-06-19

Family

ID=16690862

Family Applications (1)

Application Number Title Priority Date Filing Date
JP21659482A Pending JPS59105809A (en) 1982-12-10 1982-12-10 Concentration of liquid by membrane

Country Status (1)

Country Link
JP (1) JPS59105809A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02265628A (en) * 1989-04-05 1990-10-30 Kurita Water Ind Ltd Membranous separating process
JPH05185093A (en) * 1992-01-10 1993-07-27 Ngk Insulators Ltd Method for purifying water by using membrane
JPH05185095A (en) * 1992-01-10 1993-07-27 Ngk Insulators Ltd Water purifying treatment using membrane
KR20030000039A (en) * 2001-06-22 2003-01-06 김봉석 Device for recycling wastewater used in water jet loom and method of it
JP2008221168A (en) * 2007-03-14 2008-09-25 Fuji Electric Water Environmental Systems Co Ltd Membrane filtration method and membrane filtration apparatus

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02265628A (en) * 1989-04-05 1990-10-30 Kurita Water Ind Ltd Membranous separating process
JPH05185093A (en) * 1992-01-10 1993-07-27 Ngk Insulators Ltd Method for purifying water by using membrane
JPH05185095A (en) * 1992-01-10 1993-07-27 Ngk Insulators Ltd Water purifying treatment using membrane
KR20030000039A (en) * 2001-06-22 2003-01-06 김봉석 Device for recycling wastewater used in water jet loom and method of it
JP2008221168A (en) * 2007-03-14 2008-09-25 Fuji Electric Water Environmental Systems Co Ltd Membrane filtration method and membrane filtration apparatus

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