JPS58174282A - Treatment of waste water - Google Patents

Treatment of waste water

Info

Publication number
JPS58174282A
JPS58174282A JP5510782A JP5510782A JPS58174282A JP S58174282 A JPS58174282 A JP S58174282A JP 5510782 A JP5510782 A JP 5510782A JP 5510782 A JP5510782 A JP 5510782A JP S58174282 A JPS58174282 A JP S58174282A
Authority
JP
Japan
Prior art keywords
waste water
reverse osmosis
osmosis membrane
caustic soda
calcium
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
JP5510782A
Other languages
Japanese (ja)
Inventor
Akira Kakimoto
朗 柿本
Toshio Funakoshi
船越 俊夫
Tadaaki Tanii
谷井 忠明
Hiroyo Matsumoto
松本 曠世
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy 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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP5510782A priority Critical patent/JPS58174282A/en
Publication of JPS58174282A publication Critical patent/JPS58174282A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To prevent the clogging of a reverse osmosis membrane and to maintain the flow rate of permeated water and a high rate of desalting for a long period of time, by controlling the pH of waste water contg. calcium component and polyphosphoric acid to 4.7-4.8 then concentrating the same with the reverse osmosis membrane. CONSTITUTION:A circulation tank 1 is provided with a supply line 2 for caustic soda, a supply line 3 for sulfuric acid, a stirrer 4, and a pH controller 5 which controls the pH of the waste water in the tank by controlling the supply rate of the caustic soda and sulfuric acid. The pH of the waste water in the tank 1 is controlled to around 4.5 and since the waste water circulating in this circulation system causes a decrease in pH when subjected to a concentrating treatment in a reverse osmosis membrane device 7, the caustic soda is added thereto through a line 7. If the pH of the waste water is controlled to 4.7-4.8, the formation of calcium carbonate occuring in the calcium component and triphosphoric acid component in the waste water is eliminated and the solubility of calcium pyrophosphate is made higher.

Description

【発明の詳細な説明】 本発明は、含リン洗剤洗浄1Q液を逆浸透膜装置で濃縮
処理する場合に、炭酸力ルノウムやピロリン酸カルシウ
ム等の析出による逆浸透膜のL]づまりを防止するよう
にした処理1ノ法に関する。
Detailed Description of the Invention The present invention is designed to prevent clogging of the reverse osmosis membrane due to precipitation of carbonate, calcium pyrophosphate, etc. when concentrating phosphorus-containing detergent cleaning 1Q solution using a reverse osmosis membrane device. Regarding the first method of processing.

放射性物質を取り扱う施設に於ては、f5染された衣服
等を洗浄するため、洗剤を使用する。
In facilities that handle radioactive materials, detergents are used to wash F5-dyed clothing.

この場合として洗剤として除染性の艮いA ’Jノ洗剤
を使用しているが、この洗剤廃液を逆浸透膜により処理
する場合、従来はpH6〜7で実施しており、そのため
、炭酸カルシウムやピロリン酸カルシウムの析出があり
、膜の目づまりのため、高濃縮ができなかった。
In this case, a decontaminating A'J detergent is used as a detergent, but when this detergent waste liquid is treated with a reverse osmosis membrane, conventionally it is carried out at a pH of 6 to 7. There was precipitation of calcium pyrophosphate and membrane clogging, making it impossible to achieve high concentration.

本発明は、上記洗剤洗浄廃液処理における逆浸透膜の目
づまりを防止し、透過水量及び高説塩率を長期に渡り保
つことを目的として提案されたもので、カルンウム成分
及び重合リン酸を含む廃液を逆浸透膜によって濃縮処理
する方法において、被処理廃液のpHを予め48〜47
としたのち逆浸透膜による濃縮処理を行なうことを特徴
とする廃液処理方法を提供する。
The present invention was proposed for the purpose of preventing clogging of the reverse osmosis membrane in the above-mentioned detergent cleaning waste liquid treatment and maintaining the permeated water amount and high estimated salt rate over a long period of time. In the method of concentration treatment using a reverse osmosis membrane, the pH of the waste liquid to be treated is set to 48 to 47 in advance.
The present invention provides a method for treating waste liquid, which is characterized in that the waste liquid is then concentrated using a reverse osmosis membrane.

本発明は、上記廃液に含まれる炭酸カルシウム及びピロ
リン酸カルシウムの溶解度及び分解速度がpHにより大
きく変化する点に着目し、pHを予め48〜47に規定
した後逆漫透膜による濃縮処理を行なうことによって、
炭酸カルシウム及びピロリン酸カルシウムの沈殿を通常
の洗剤排液中リン濃度では、減容比(逆浸透膜処理餌の
被処理液の体積/逆浸透膜処理後の被処理液の体積)2
0以上に確実に達成できる゛。
The present invention focuses on the fact that the solubility and decomposition rate of calcium carbonate and calcium pyrophosphate contained in the above waste liquid vary greatly depending on the pH, and after the pH is predefined at 48 to 47, concentration treatment is performed using an inverse permeable membrane. By,
The precipitation of calcium carbonate and calcium pyrophosphate is reduced by the volume reduction ratio (volume of treated liquid of reverse osmosis membrane treated bait/volume of treated liquid after reverse osmosis membrane treatment) at the phosphorus concentration in normal detergent wastewater.
You can definitely achieve 0 or more.

次に本発明方法の一実施例を図面に基いて説明する。Next, an embodiment of the method of the present invention will be explained based on the drawings.

第1図に示す逆浸透膜濃縮装置を使用して含リン洗剤を
液を濃縮処理した。第1図において。
The phosphorus-containing detergent solution was concentrated using the reverse osmosis membrane concentrator shown in FIG. In FIG.

!は循環タンクで、カセイソーダ供給うイ/2゜硫酸供
給ライン8.かく拌機4.及びカセイソーダ及び硫酸の
供給量を調節してタンク内廃液のpHを調節するp)(
調節計5を具備する。6は循環タンクl内の廃液を逆浸
透膜装置7に送る高圧ポンプ、8はS液を循環タンクl
に戻す1Vk環ライノ10に設けられたIF力調整弁、
9は冷却器である。
! is a circulation tank that supplies caustic soda/2° sulfuric acid supply line 8. Stirrer 4. and adjusting the supply amount of caustic soda and sulfuric acid to adjust the pH of the waste liquid in the tank p) (
A controller 5 is provided. 6 is a high-pressure pump that sends the waste liquid in the circulation tank l to the reverse osmosis membrane device 7, and 8 is the S liquid that is sent to the circulation tank l.
IF force adjustment valve installed in 1Vk Ring Rhino 10,
9 is a cooler.

このような装置において、循環タックl内の廃液のpH
を45付近に調整する。なおこの循環上 系を循環する廃液は逆浸透膜装置7での濃縮処理によっ
てpHの低下が起るためライン2よりカセイソーダを添
加する。
In such a device, the pH of the waste liquid in the circulating tack is
Adjust to around 45. Caustic soda is added to the waste liquid circulating through the circulation system through line 2 because its pH decreases due to concentration treatment in the reverse osmosis membrane device 7.

洗剤廃液中には、カルシウム成分及び、三リン酸H6P
gO1oが存在し、下記の反応式に示す反応が起り沈殿
を生成する。
Calcium components and triphosphate H6P are present in detergent waste liquid.
gO1o is present, and the reaction shown in the reaction formula below occurs to produce a precipitate.

Ca + C!Os  →CaC0@↓ ・・・・・・
・・・・・・・・・・・・(1)Hy、Pgolo +
)(to −) H3PO3+H<?Ot −(2)H
4P207+H20→2H,PO4・・・・・・・・・
・・・・・・(3)P207’  + 2Ca  −C
a2Pt0r−−−・・・・・・(4)この沈殿の内、
(1)式で生成する炭酸力ルンウムはpHを58以下に
する事により1次式(5)の反応が起り9分解する。
Ca+C! Os →CaC0@↓ ・・・・・・
・・・・・・・・・・・・(1) Hy, Pgolo +
)(to −) H3PO3+H<? Ot-(2)H
4P207+H20→2H, PO4・・・・・・・・・
......(3) P207' + 2Ca -C
a2Pt0r --- (4) Of this precipitate,
By lowering the pH to 58 or less, the carbonic acid produced by formula (1) undergoes the reaction of linear formula (5) and decomposes by 9.

CaCOH+ 2H→Ca +H20+ 002↑−(
5)また式(4)により生成するピロリン酸カルンウム
Ca2P20yの溶解度は第2図のように−なる。
CaCOH+ 2H→Ca +H20+ 002↑-(
5) Also, the solubility of carunium pyrophosphate Ca2P20y produced by formula (4) is as shown in FIG.

通常、IS剤中の三リン酸含有量はリンとして5〜10
重量%であり、廃水中濃度と1では、洗剤濃度800 
ppmである。この内、ピロリン酸力ルノウムの生成量
は式(2)より、最大278である。しかし9式(3)
の分解反応もあり、実験値では最大でl/2であった。
Usually, the triphosphoric acid content in IS agents is 5 to 10% as phosphorus.
% by weight, and when the concentration in wastewater is 1, the detergent concentration is 800
It is ppm. Of these, the maximum amount of pyrophosphate produced is 278, according to equation (2). However, formula 9 (3)
There was also a decomposition reaction, and experimental values showed a maximum of 1/2.

この結果、ピロリン酸の生成量は第8図に示す濃度であ
ろうと考えられ、pH4,7時の溶解度約700 pp
m以上になる減容比は、20以−Fであるので、$容比
が20以−F、となるまでピロリン酸力ルンウムの沈殿
は生じない。
As a result, the amount of pyrophosphoric acid produced is thought to be at the concentration shown in Figure 8, with a solubility of approximately 700 pp at pH 4.7.
Since the volume reduction ratio of m or more is 20 or more -F, precipitation of pyrophosphate does not occur until the volume ratio becomes 20 or more -F.

以上のように本発明では、被処理を液のp+lをFめ4
8〜47とする事により、炭酸力ルンウムの生成を無ク
シ、又、ピロリン酸力ルノウムの溶解度を高くする事が
できる。これを模擬洗浄廃液により実験した結果を第4
図叉び第5図に示す。この結果からpHを低(する稈透
過水量の低下が少ない事が明瞭にわかる。この実験にお
けるP、O,、初期濃度はリンとして38 ppmであ
る。
As described above, in the present invention, the p+l of the liquid to be treated is
By setting it to 8 to 47, it is possible to prevent the formation of carbonate and increase the solubility of pyrophosphate. The results of an experiment using simulated cleaning waste liquid are shown in the fourth section.
This is shown in Figure 5. From this result, it is clearly seen that the decrease in the amount of water permeated through the culm is small when the pH is lowered.The initial concentration of P, O, and phosphorus in this experiment was 38 ppm as phosphorus.

礁 なおpHが酸性側になれば配管、熾烈類の腐食が生じる
ためむやみに低くすることは出来ない。
However, if the pH becomes acidic, piping and corrosion will occur, so it cannot be lowered unnecessarily.

第2図の溶解度からpH4,5±02の範囲が好ましい
Based on the solubility shown in FIG. 2, a pH range of 4.5±02 is preferable.

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

第1図は本発明方法の一実施例を実施する逆浸透膜濃縮
装置を示すフローチャート、第2図はピロリン酸カルシ
ウムの溶解度を示す線図。 第8図は濃縮廃液中P!O,の最大濃度を示す線図。 第4図及び第5図は本発明方法を模擬洗浄廃液により実
験した場合の結果を示す線図である。 l・・・循環タンク、6・・・高圧ポンプ、7・・・逆
浸透膜装置、8・・・圧力調整弁、9・・・冷却器、1
0・・・循環ライン。 PH 系容比 第3図 第4図 第5ゾ
FIG. 1 is a flowchart showing a reverse osmosis membrane concentrator for carrying out an embodiment of the method of the present invention, and FIG. 2 is a diagram showing the solubility of calcium pyrophosphate. Figure 8 shows P in concentrated waste liquid! Diagram showing the maximum concentration of O. FIGS. 4 and 5 are diagrams showing the results of experiments using the method of the present invention using simulated cleaning waste liquid. l...Circulation tank, 6...High pressure pump, 7...Reverse osmosis membrane device, 8...Pressure adjustment valve, 9...Cooler, 1
0... Circulation line. PH system volume ratio Figure 3 Figure 4 Figure 5

Claims (1)

【特許請求の範囲】 カルンウム成分及び1重合リン酸を含む廃液を逆浸透膜
によって濃縮処理する方法において。 被処理廃液のpHを予め48〜4.7としたのち逆浸透
膜による濃縮処理を行なうことを特徴とする廃液処理方
法。
[Claims] A method for concentrating a waste liquid containing a carunium component and monopolymerized phosphoric acid using a reverse osmosis membrane. A waste liquid treatment method characterized in that the pH of the waste liquid to be treated is adjusted to 48 to 4.7 in advance and then concentrated using a reverse osmosis membrane.
JP5510782A 1982-04-02 1982-04-02 Treatment of waste water Pending JPS58174282A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5510782A JPS58174282A (en) 1982-04-02 1982-04-02 Treatment of waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5510782A JPS58174282A (en) 1982-04-02 1982-04-02 Treatment of waste water

Publications (1)

Publication Number Publication Date
JPS58174282A true JPS58174282A (en) 1983-10-13

Family

ID=12989524

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5510782A Pending JPS58174282A (en) 1982-04-02 1982-04-02 Treatment of waste water

Country Status (1)

Country Link
JP (1) JPS58174282A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008188498A (en) * 2007-02-01 2008-08-21 Kobelco Eco-Solutions Co Ltd Treatment method and treatment equipment for water to be treated

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008188498A (en) * 2007-02-01 2008-08-21 Kobelco Eco-Solutions Co Ltd Treatment method and treatment equipment for water to be treated
JP4536740B2 (en) * 2007-02-01 2010-09-01 株式会社神鋼環境ソリューション Treatment method and treatment equipment for treated water

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