JPH0810777A - Bubbling device for waste water of backwashing of portable water forming device - Google Patents

Bubbling device for waste water of backwashing of portable water forming device

Info

Publication number
JPH0810777A
JPH0810777A JP14466794A JP14466794A JPH0810777A JP H0810777 A JPH0810777 A JP H0810777A JP 14466794 A JP14466794 A JP 14466794A JP 14466794 A JP14466794 A JP 14466794A JP H0810777 A JPH0810777 A JP H0810777A
Authority
JP
Japan
Prior art keywords
water
carbon dioxide
backwash
backwashing
line
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.)
Withdrawn
Application number
JP14466794A
Other languages
Japanese (ja)
Inventor
Takaharu Yamada
孝晴 山田
Hiroshi Hamada
紘 浜田
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 JP14466794A priority Critical patent/JPH0810777A/en
Publication of JPH0810777A publication Critical patent/JPH0810777A/en
Withdrawn legal-status Critical Current

Links

Abstract

PURPOSE:To suppress backwashing water to alkaline concn. and to shorten the time for treating waste water of backwashing by bubbling a vent gas contg. carbon dioxide in the waste water of backwashing of a thickening tank of a device for forming raw water into potable water by supplying of the carbon dioxide into the raw water and treating in a limestone filter. CONSTITUTION:The raw water for the potable water is fed from a feed water line 6 and is partly sent to a carbon dioxide absorption column 1 where the carbon dioxide is absorbed in the raw water and thereafter, the water is again joined with the feed water line 6. Next, the raw water is sent to a limestone absorption filter column 20 and is passed through the limestone filter 2 by which the raw water is filtered. The supply of the raw water is stopped and the backwashing water is supplied by starting a backwashing pump 5 to backwash the filter 2 when the limestone filter 2 is clogged. At this time, a gas supply valve 8 is opened to supply the vent gas contg. some carbon dioxide into the thickening tank 3 through an acidic gas line 4 and to eject the carbon dioxide into the waste water of backwashing, by which the waste water of backwashing is neutralized to pH <=7.9 with the carbon dioxide and the suspended solids are rapidly settled.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は原水への炭酸ガスの供給
と石灰石フィルタでの処理により原水を飲料水化する装
置における、石灰石フィルタの逆洗排水用バブリング装
置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a bubbling device for backwash drainage of a limestone filter in a device for converting raw water into drinking water by supplying carbon dioxide gas to raw water and treating with a limestone filter.

【0002】[0002]

【従来の技術】従来の原水飲料水化装置の概要を図2に
示す。原水は給水ライン6より送水され、この原水の一
部は炭酸ガス吸収塔1へ送られ、ここで炭酸ガスを吸収
して再度給水ライン6へ戻し原水と混合される。この炭
酸ガスを吸収した原水は炭酸カルシウムを充填した石灰
石フィルタ塔20へ送水され、ここで石灰石フィルタ2
を通過中に炭酸カルシウムが溶解するため、炭酸カルシ
ウムを含有する処理水(飲料水)となって前記石灰石フ
ィルタ塔20の下部に接続した処理水ライン17から排
出される。一方、石灰石フィルタ2は付着したゴミを除
去し、炭酸カルシウムを補充するため、1週間に1回程
度逆洗する必要がある。このため石灰石フィルタ塔20
への飲料水原水の通水を停止した後、逆洗ポンプ5を起
動させて石灰石フィルタ塔20の下部に接続する逆洗水
供給ライン13から逆洗水を送り石灰石フィルタ2を逆
洗する。逆洗水の供給は石灰石フィルタ塔20の下部に
接続する処理水ライン17及び逆洗水供給ライン13に
設置された弁の切替えによって行われる。石灰石フィル
タ塔20の上部から排出される逆洗排水は逆洗排水ライ
ン18を通って濃縮槽3へ送られる。逆洗排水は濃縮槽
3中で数時間静置し、抜出弁10を上から下へ順次開い
て上澄み液のみを回収ライン15から回収ポンプ7で抜
き出して回収し、砂ろ過器12を通した後、再度飲料水
原水として給水ライン6へ戻される。一方、濃縮槽3に
沈殿した堆積物はスラリポンプ14により別途排出され
る。一般的にこのような飲料水化装置は、複数の石灰石
フィルタ塔20と1基の濃縮槽3により構成されてい
る。
2. Description of the Related Art An outline of a conventional raw water drinking water conversion apparatus is shown in FIG. The raw water is sent from the water supply line 6, a part of the raw water is sent to the carbon dioxide absorption tower 1, where the carbon dioxide is absorbed and returned to the water supply line 6 again to be mixed with the raw water. The raw water that has absorbed this carbon dioxide is sent to a limestone filter tower 20 filled with calcium carbonate, where the limestone filter 2
Calcium carbonate is dissolved during passage through the treated water, so that treated water (drinking water) containing calcium carbonate is discharged from the treated water line 17 connected to the lower portion of the limestone filter tower 20. On the other hand, the limestone filter 2 needs to be backwashed about once a week in order to remove adhered dust and supplement calcium carbonate. Therefore, the limestone filter tower 20
After stopping the passage of the raw water to the drinking water, the backwash pump 5 is activated to feed backwash water from the backwash water supply line 13 connected to the lower portion of the limestone filter tower 20 to backwash the limestone filter 2. The backwash water is supplied by switching the valves installed in the treated water line 17 and the backwash water supply line 13 connected to the lower part of the limestone filter tower 20. The backwash drainage discharged from the upper part of the limestone filter tower 20 is sent to the concentration tank 3 through the backwash drainage line 18. The backwash drainage is allowed to stand for several hours in the concentrating tank 3, the extraction valve 10 is sequentially opened from top to bottom, and only the supernatant liquid is extracted from the recovery line 15 by the recovery pump 7 and recovered, and then passed through the sand filter 12. After that, it is returned to the water supply line 6 as drinking water raw water again. On the other hand, the sediment deposited in the concentration tank 3 is separately discharged by the slurry pump 14. Generally, such a drinking water liquefying device is composed of a plurality of limestone filter towers 20 and one concentrating tank 3.

【0003】[0003]

【発明が解決しようとする課題】このような原水の飲料
水化プロセスにおいて、逆洗排水は逆洗開始後しばらく
すると炭酸カルシウムがほぼ飽和状態まで溶解し、排水
のpHが8.2程度にまで上昇し、乳白色の浮遊固形物
(炭酸カルシウムが主成分)が発生する。この浮遊固形
物は有害物ではないが、水が白く濁るためそのままでは
飲料水として使えないので濃縮槽で浮遊固形物を沈殿さ
せ、上澄み液のみを採取する必要がある。ところがこの
浮遊固形物はpHが7.9以下の場合には沈降速度は速
いが、pHが7.9を越えると沈降速度が格段に遅くな
る。そのため濃縮槽での静置に5〜6時間という長時間
を要していた。静置に長時間を要すると1日に1基の石
灰石フィルタ塔しか処理できないことになり、一度に複
数の石灰石フィルタ塔を逆洗するのは不可能であった
(例えば、石灰石フィルタ塔が14基設置されているプ
ロセスでは、毎日2基ずつの逆洗を必要とする)。ま
た、濃縮槽3には深さ方向に複数個の抜き出し弁10を
設置し、静置時間経過とともに上部から下部へとタイマ
ーにより開閉して、上澄み液を抜いていた。さらに、回
収を速めるためには、pH調整用として特殊薬品(酸
液)を用いる必要があった。しかし、回収を速めると沈
降が不十分であるため、回収液に浮遊固形物が若干混入
することもあり、上澄み水の回収ポンプの下流側に砂ろ
過器12を設置する必要があった。
In such a drinking water conversion process of raw water, the backwash drainage dissolves calcium carbonate to a substantially saturated state after a while after the start of backwashing, and the pH of the drainage reaches about 8.2. As a result, milky white floating solids (mainly calcium carbonate) are generated. Although this suspended solid is not a harmful substance, it cannot be used as drinking water as it is because the water is white and turbid, so it is necessary to precipitate the suspended solid in the concentration tank and collect only the supernatant. However, when the pH of the suspended solids is 7.9 or less, the sedimentation speed is fast, but when the pH exceeds 7.9, the sedimentation speed is significantly slowed. Therefore, it took a long time of 5 to 6 hours to stand still in the concentration tank. If it takes a long time to stand, only one limestone filter tower can be processed per day, and it is impossible to backwash a plurality of limestone filter towers at a time (for example, if the limestone filter tower is 14 The base installed process requires two backwashes each day). Further, a plurality of withdrawal valves 10 were installed in the concentration tank 3 in the depth direction, and the supernatant liquid was withdrawn by opening and closing with a timer from the upper part to the lower part with the passage of standing time. Furthermore, in order to speed up recovery, it was necessary to use a special chemical (acid solution) for pH adjustment. However, if the recovery is accelerated, the sedimentation is insufficient, and thus some of the suspended solids may be mixed in the recovered liquid, and it was necessary to install the sand filter 12 on the downstream side of the supernatant water recovery pump.

【0004】本発明は前記従来技術における問題点を解
決し、濃縮槽での滞留所要時間が短くてすみ、中和用の
薬品を必要とせず、しかも設備も簡略化された原水の飲
料水化装置を提供することを目的とする。
The present invention solves the above-mentioned problems in the prior art, requires only a short residence time in the concentrating tank, does not require a chemical for neutralization, and simplifies the equipment. The purpose is to provide a device.

【0005】[0005]

【課題を解決するための手段】本発明は、炭酸ガス吸収
塔を備えた飲料水用原水の給水ラインと、該給水ライン
に接続する石灰石フィルタ塔と、該フィルタ塔から出る
処理水を排出する処理水ラインよりなる飲料水化系と、
該フィルタ塔の処理水ライン側に接続する逆洗水供給ラ
インと、該フィルタ塔の上部に接続する逆洗排水ライン
と、逆洗排水を受けて固形物を濃縮分離する濃縮槽と、
該濃縮槽に接続する上澄み液回収ライン及びスラリ排出
ラインよりなる石灰石フィルタ逆洗系によって構成され
る原水の飲料水化装置において、前記炭酸ガス吸収塔か
ら排出される炭酸ガス含有ガスを前記濃縮槽に導く酸性
ガスライン、酸性ガスの供給量を調整するガス供給弁及
び該酸性ガスを濃縮槽内の逆洗排水中にバブリングさせ
るバブリング管よりなることを特徴とする飲料水化装置
の逆洗排水用バブリング装置である。
According to the present invention, a raw water supply line for drinking water having a carbon dioxide absorption tower, a limestone filter tower connected to the water supply line, and treated water discharged from the filter tower are discharged. A drinking water system consisting of treated water lines,
A backwash water supply line connected to the treated water line side of the filter tower, a backwash drainage line connected to the upper part of the filter tower, and a concentrating tank that receives backwash drainage to concentrate and separate solid matter,
In a drinking water hydration apparatus for raw water constituted by a limestone filter backwash system consisting of a supernatant recovery line and a slurry discharge line connected to the concentrating tank, the carbon dioxide-containing gas discharged from the carbon dioxide absorption tower is converted into the concentrating tank. Backwash drainage of a drinking water treatment apparatus, characterized by comprising an acid gas line leading to the tank, a gas supply valve for adjusting the supply amount of acid gas, and a bubbling pipe for bubbling the acid gas during backwash drainage in the concentration tank. Bubbling device.

【0006】以下、図面を参照して本発明の装置を詳細
に説明する。図1は本発明の逆洗排水用バブリング装置
を組み込んだ原水の飲料水化装置の概略を示す系統図で
ある。図1の装置において、飲料水原水を給水ライン6
から送水する。この原水の一部は途中で炭酸ガス吸収塔
1へ送られ、炭酸ガスを吸収させて再度給水ライン6へ
合流する。次に飲料水原水は石灰石フィルタ塔20へ送
水され、ここで炭酸カルシウムを充填した石灰石フィル
タ2を通過してろ過される。このとき炭酸カルシウムが
溶解し、炭酸カルシウムを含有した処理水となって前記
塔20下部より出て、処理水ライン17より排出され
る。
The device of the present invention will be described below in detail with reference to the drawings. FIG. 1 is a system diagram showing an outline of a drinking water conversion device for raw water incorporating the bubbling device for backwash drainage of the present invention. In the apparatus of FIG. 1, the raw water for drinking water is supplied to the water supply line 6
Water from. A part of this raw water is sent to the carbon dioxide absorption tower 1 on the way, absorbs the carbon dioxide and joins the water supply line 6 again. Next, the raw drinking water is sent to a limestone filter tower 20, where it is filtered through a limestone filter 2 filled with calcium carbonate. At this time, calcium carbonate is dissolved to form treated water containing calcium carbonate, which is discharged from the lower part of the tower 20 and discharged from the treated water line 17.

【0007】一方、石灰石フィルタ2に目詰まりが生じ
たり、炭酸カルシウムの溶出量が少なくなった場合には
原水の供給を中止し、逆洗ポンプ5を起動させて逆洗水
供給ライン13から逆洗水を供給し、石灰石フィルタ塔
20の石灰石フィルタ2を逆洗する。逆洗水は石灰石フ
ィルタ塔20に接続された弁を調整することにより石灰
石フィルタ塔20の下部より注入され、上部より排出さ
れる。排出された逆洗水は逆洗排水ライン18を経て濃
縮槽3へ送られる。本発明においては、炭酸ガス吸収塔
1の頂部のベントラインにガス供給弁8及びガス放出弁
9を設け、濃縮槽3の逆洗排水を静置する直前に、ガス
供給弁8を開に、ガス放出弁9を閉とし、炭酸ガスを若
干含んでいるベントガスを、酸性ガスライン4を通し濃
縮槽3の下部へ供給し、下部のバブリング管11より逆
洗排水中へ供給することを特徴としている。濃縮槽3中
でバブリングされた逆洗排水は炭酸ガスにより中和され
てpHが7.9以下になるので、短い静置時間で浮遊固
形物を沈降させることができる。浮遊固形物を沈降させ
た後、抜出弁10を開き、回収ライン15から上澄み水
のみを回収ポンプ7で抜き出す。この回収水は再度飲料
水原水ラインへ戻すことができる。一方、濃縮槽3に沈
殿した堆積物はスラリポンプ14により別途排出され
る。
On the other hand, when the limestone filter 2 is clogged or the elution amount of calcium carbonate becomes small, the supply of raw water is stopped and the backwash pump 5 is started to reverse the backwash water supply line 13. Wash water is supplied to backwash the limestone filter 2 of the limestone filter tower 20. The backwash water is injected from the lower part of the limestone filter tower 20 by adjusting the valve connected to the limestone filter tower 20, and discharged from the upper part. The discharged backwash water is sent to the concentration tank 3 through the backwash drain line 18. In the present invention, the gas supply valve 8 and the gas release valve 9 are provided in the vent line at the top of the carbon dioxide absorption tower 1, and the gas supply valve 8 is opened immediately before the backwash drainage of the concentration tank 3 is allowed to stand. The gas release valve 9 is closed, and a vent gas containing a small amount of carbon dioxide is supplied to the lower part of the concentration tank 3 through the acid gas line 4 and is supplied to the backwash drainage from the lower bubbling pipe 11. There is. The backwash wastewater bubbled in the concentrating tank 3 is neutralized with carbon dioxide gas to have a pH of 7.9 or less, so that suspended solids can be settled in a short standing time. After the suspended solids are settled, the extraction valve 10 is opened, and only the supernatant water is extracted from the recovery line 15 by the recovery pump 7. This recovered water can be returned to the drinking water raw water line again. On the other hand, the sediment deposited in the concentration tank 3 is separately discharged by the slurry pump 14.

【0008】[0008]

【作用】濃縮槽3の逆洗排水の中で炭酸ガスを含むベン
トガスをバブリングすることにより、逆洗水のpHを
7.9以下に抑えることができる。pHが7.9以下に
抑えられると、排水中の浮遊固形分の沈降速度が速まる
とともに、浮遊固形物中の炭酸カルシウムはバブリング
された炭酸ガスにより溶出し、重炭酸カルシウムになる
ので、上澄み水はpHが7.9を超えた場合のものに比
べ、格段に浄化される。
By bubbling a vent gas containing carbon dioxide gas in the backwash water of the concentration tank 3, the pH of the backwash water can be suppressed to 7.9 or less. When the pH is suppressed to 7.9 or less, the sedimentation rate of the suspended solids in the wastewater is increased, and the calcium carbonate in the suspended solids is eluted by the bubbled carbon dioxide gas to become calcium bicarbonate. Is significantly purified compared to the case where the pH exceeds 7.9.

【0009】[0009]

【発明の効果】本発明の装置を使用することにより次の
ような効果がある。 逆洗排水の沈降速度を速めることが可能となり、1基
の濃縮槽でも1日複数基の逆洗が可能となる。 排水のpHを下げるのに、放出ガス中の炭酸ガスをバ
ブリング混入するため、排水のpHを7.9以下に下げ
ることができ、特殊薬品(酸液)を使用する必要がな
く、薬品費用が不要である。 濃縮槽からの逆洗排水は静置が完全であるため、従来
必要であった砂ろ過器が不要となり、設備費用を低減で
きる。 沈降が速いため排水用抜き出し弁の個数を減じること
ができ、設備費用を低減できる。
The following effects can be obtained by using the device of the present invention. It is possible to increase the sedimentation rate of the backwash drainage, and it is possible to backwash a plurality of units per day even with one concentration tank. In order to lower the pH of the wastewater, bubbling carbon dioxide gas in the released gas, the pH of the wastewater can be lowered to 7.9 or less, and it is not necessary to use a special chemical (acid solution), and the chemical cost is low. It is unnecessary. Since the backwash drainage from the concentrating tank is completely stationary, the sand filter, which was required in the past, is not required, and the equipment cost can be reduced. Since settling is fast, the number of drainage extraction valves can be reduced, and equipment costs can be reduced.

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

【図1】本発明の逆洗排水用バブリング装置を組み込ん
だ原水の飲料水化装置の概略を示す系統図。
FIG. 1 is a system diagram showing an outline of a drinking water conversion device for raw water incorporating a bubbling device for backwash drainage of the present invention.

【図2】従来の原水の飲料水化装置の1例を示す概略系
統図。
FIG. 2 is a schematic system diagram showing one example of a conventional raw water drinking water conversion device.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 炭酸ガス吸収塔を備えた飲料水用原水の
給水ラインと、該給水ラインに接続する石灰石フィルタ
塔と、該フィルタ塔から出る処理水を排出する処理水ラ
インよりなる飲料水化系と、該フィルタ塔の処理水ライ
ン側に接続する逆洗水供給ラインと、該フィルタ塔の上
部に接続する逆洗排水ラインと、逆洗排水を受けて固形
物を濃縮分離する濃縮槽と、該濃縮槽に接続する上澄み
液回収ライン及びスラリ排出ラインよりなる石灰石フィ
ルタ逆洗系によって構成される原水の飲料水化装置にお
いて、前記炭酸ガス吸収塔から排出される炭酸ガス含有
ガスを前記濃縮槽に導く酸性ガスライン、酸性ガスの供
給量を調整するガス供給弁及び該酸性ガスを濃縮槽内の
逆洗排水中にバブリングさせるバブリング管よりなるこ
とを特徴とする飲料水化装置の逆洗排水用バブリング装
置。
1. A drinking water conversion system comprising a raw water supply line for drinking water provided with a carbon dioxide absorption tower, a limestone filter tower connected to the water supply line, and a treated water line for discharging treated water from the filter tower. A system, a backwash water supply line connected to the treated water line side of the filter tower, a backwash drain line connected to the upper part of the filter tower, and a concentration tank for concentrating and separating solid matter by receiving backwash drainage. In a drinking water hydration apparatus for raw water constituted by a limestone filter backwash system consisting of a supernatant recovery line connected to the concentration tank and a slurry discharge line, the carbon dioxide-containing gas discharged from the carbon dioxide absorption tower is concentrated as described above. A beverage characterized by comprising an acid gas line leading to a tank, a gas supply valve for adjusting the supply amount of the acid gas, and a bubbling pipe for bubbling the acid gas into the backwash drainage in the concentration tank. Bubbling device for backwash drainage of hydration equipment.
JP14466794A 1994-06-27 1994-06-27 Bubbling device for waste water of backwashing of portable water forming device Withdrawn JPH0810777A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP14466794A JPH0810777A (en) 1994-06-27 1994-06-27 Bubbling device for waste water of backwashing of portable water forming device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP14466794A JPH0810777A (en) 1994-06-27 1994-06-27 Bubbling device for waste water of backwashing of portable water forming device

Publications (1)

Publication Number Publication Date
JPH0810777A true JPH0810777A (en) 1996-01-16

Family

ID=15367436

Family Applications (1)

Application Number Title Priority Date Filing Date
JP14466794A Withdrawn JPH0810777A (en) 1994-06-27 1994-06-27 Bubbling device for waste water of backwashing of portable water forming device

Country Status (1)

Country Link
JP (1) JPH0810777A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6338561B1 (en) 1998-01-29 2002-01-15 Nippon Seiki Co., Ltd. Luminous pointer

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6338561B1 (en) 1998-01-29 2002-01-15 Nippon Seiki Co., Ltd. Luminous pointer

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