JP3439576B2 - River purification method and purification device - Google Patents

River purification method and purification device

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Publication number
JP3439576B2
JP3439576B2 JP20474595A JP20474595A JP3439576B2 JP 3439576 B2 JP3439576 B2 JP 3439576B2 JP 20474595 A JP20474595 A JP 20474595A JP 20474595 A JP20474595 A JP 20474595A JP 3439576 B2 JP3439576 B2 JP 3439576B2
Authority
JP
Japan
Prior art keywords
river
water
weir
packed bed
waterway
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.)
Expired - Fee Related
Application number
JP20474595A
Other languages
Japanese (ja)
Other versions
JPH0947770A (en
Inventor
克之 片岡
正英 高田
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.)
Ebara Corp
Original Assignee
Ebara Corp
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Filing date
Publication date
Application filed by Ebara Corp filed Critical Ebara Corp
Priority to JP20474595A priority Critical patent/JP3439576B2/en
Publication of JPH0947770A publication Critical patent/JPH0947770A/en
Application granted granted Critical
Publication of JP3439576B2 publication Critical patent/JP3439576B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Biological Treatment Of Waste Water (AREA)

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は有機物で汚染された
河川の浄化技術に関するものであり、河川水を従来より
著しく高速度で浄化できる新技術に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a technique for purifying a river polluted with organic substances, and relates to a new technique capable of purifying river water at a significantly higher speed than ever before.

【0002】[0002]

【従来の技術】下水道および合併浄化槽が普及していな
い市町村を流れる河川には家庭からの雑排水(台所排
水、風呂排水など)が流入するため有機物で汚染され
る。人口増加にともない汚染度はますますひどくなって
おり河川が下水化している例も多い。このような汚濁河
川は不快であるばかりでなく川に住む多くの生物に悪影
響を及ぼし、下流に上水道の取水源がある場合には飲料
水を汚染する。
2. Description of the Related Art Domestic sewage (kitchen drain, bath drain, etc.) flows into rivers that run through municipalities where sewers and combined septic tanks have not spread, and is contaminated with organic substances. The pollution level is getting worse with the increase of the population, and there are many cases where rivers are sewage. Such polluted rivers are not only unpleasant, but also adversely affect many living organisms in the river and contaminate drinking water if there is a water supply source downstream.

【0003】そのため最近、河川を直接浄化する試みが
種々なされているが、まだ決定的な技術は開発されてい
ない。従来の技術は「礫間接触浄化法」が代表的な技術
である。この技術は大粒径(数センチ)の砕石を河川敷
に設けた河川水路(河川本流から分岐させる)に大量に
充填し、河川水を4〜5時間かけて水平方向にゆっくり
と流下させるものである。しかし、浄化に要する時間が
長いため、大量の砕石と大きな設置面積を必要とし、水
量が少ない小河川以外には適用が困難であった。また砕
石充填部に捕捉された汚泥の除去が面倒であった。砕石
の代わりにハニカムチュ−ブ、繊維をモ−ル状に束ねた
ものなどの各種充填剤が検討されているが礫間接触酸化
法と同様の欠点を持っている。
Therefore, various attempts have been made recently to directly purify rivers, but no definitive technique has been developed yet. A typical conventional technique is the “catalyst contact purification method”. This technology fills a large amount of crushed stone with a large particle size (several centimeters) into a river channel (branching from the main stream of a river) and slowly flows down the river water horizontally for 4 to 5 hours. is there. However, since it takes a long time to clean up, a large amount of crushed stones and a large installation area were required, and it was difficult to apply it except to small rivers with a small amount of water. Moreover, the removal of sludge trapped in the crushed stone filling part was troublesome. Various fillers such as a honeycomb tube and a bundle of fibers bundled in place of crushed stone have been studied, but they have the same drawbacks as the gravel contact oxidation method.

【0004】[0004]

【発明が解決しようとする課題】本発明は従来よりも大
幅に短時間(10分程度)で効果的に汚濁河川で浄化で
き、汚泥の除去にも容易な新技術を提供するものであ
る。
DISCLOSURE OF THE INVENTION The present invention provides a new technique that can be effectively purified in a polluted river in a significantly shorter time (about 10 minutes) than before, and is also easy to remove sludge.

【0005】[0005]

【課題を解決するための手段】上記課題は以下の発明に
より達成された。すなわち、 (1)河川または水路を横断し、水中に沈没して配置し
た比重が0.85以上1未満の浮上充填剤の充填層に該
河川または水路の水を通過させ、該水中の濁質及び/ま
たは有機物を除去するとともに、前記充填層に供給する
前記水及び/または空気量を増大させて該充填層を洗浄
し、該洗浄排水を該河川または水路の系外に導いて固液
分離した後、分離液は該河川または水路に返送すること
を特徴とする河川の浄化方法。 (2)1)河川または水路を横断する第1の堰と 2)第1の堰の上流側に第1の堰と平行して河川または
水路を横断配置され、且つ下方に開口部を設けた第2の
堰と 3)前記両堰の間に沈没配備した比重が0.85以上1
未満の浮上充填剤の充填層と 4)第2の堰の水面と前記充填層頂端の高さ位置に開口
する開閉手段を備えた洗浄排水管と 5)該河川または水路の系外に配置される該洗浄排水管
に連通する固液分離装置と 6)該固液分離装置から分離水を該河川または水路に排
出する配管を備えたことを特徴とする河川の浄化装置。
The above-mentioned objects have been achieved by the following inventions. That is, (1) the water in the river or water channel is passed through a packed bed of floating filler having a specific gravity of 0.85 or more and less than 1 which is disposed by being submerged in the water across the river or water channel, and turbidity in the water And / or organic substances are removed, and the amount of water and / or air supplied to the packed bed is increased to wash the packed bed, and the washing wastewater is guided to the outside of the system of the river or water channel to perform solid-liquid separation. After that, the separated liquid is returned to the river or waterway. (2) 1) a first weir that crosses a river or a waterway, and 2) an upstream side of the first weir, which is arranged across the river or a waterway in parallel with the first weir, and has an opening below 3) The second weir and 3) The specific gravity of the sunken and deployed weir is 0.85 or more 1
And less than 4) a packed bed of floating filler and 4) a cleaning drainage pipe provided with opening / closing means opening at the height of the water surface of the second weir and the top end of the packed bed, and 5) arranged outside the system of the river or waterway. 6. A river purification device comprising: a solid-liquid separation device communicating with the washing / drainage pipe; and 6) a pipe for discharging separated water from the solid-liquid separation device to the river or a waterway.

【0006】(3)前記充填層の下方に空気を導入する
曝気手段を配備したことを特徴とする上記(2)記載の
河川の浄化装置。 (4)前記第2の堰が下方の開口部に開閉自在に設けら
れるゲ−トを有することを特徴とする上記(2)記載の
河川の浄化装置。 (5)前記ゲ−トが横断方向に複数に分割され個々に開
閉自在に設けられることを特徴とする上記(4)記載の
河川の浄化装置。 (6)前記充填層が前記ゲ−トに対応して複数に分割さ
れ対応するゲ−トからのみ通水されることを特徴とする
上記(5)記載の河川の浄化装置。 (7)前記固液分離装置が沈殿装置であることを特徴と
する上記(2)記載の河川の浄化装置。 (8)充填層の洗浄に際し、前記曝気手段からの空気吹
き込み量を増大させることを特徴とする上記(1)記載
の河川の浄化方法。 (9)上記(5)記載の河川の浄化装置の充填層の洗浄
に際し、一部のゲ−トを閉、残りのゲ−トを開として、
充填層への通水量および/または通水位置を変化させる
ことを特徴とする上記(1)記載の河川の浄化方法。
(3) The river purifier according to the above (2), characterized in that an aeration means for introducing air is provided below the packed bed. (4) The river purifier according to the above (2), wherein the second weir has a gate that is openably and closably provided in the lower opening. (5) The river purifier according to the above (4), wherein the gate is divided into a plurality of pieces in the transverse direction and provided so as to be opened and closed individually. (6) The river purification device according to (5), wherein the packed bed is divided into a plurality of parts corresponding to the gates and water is passed only from the corresponding gates. (7) The river purification device according to (2) above, wherein the solid-liquid separation device is a precipitation device. (8) The method for purifying a river according to (1) above, wherein the amount of air blown from the aeration means is increased when the packed bed is washed. (9) When washing the packed bed of the river purification apparatus described in (5) above, some gates are closed and the remaining gates are opened,
The method for purifying a river according to (1) above, wherein the amount of water flow and / or the position of water flow to the packed bed is changed.

【0007】なお、上記(9)記載の河川の浄化方法を
より効果的に行うため充填槽下方に固定及び/又は可動
式構造物(バッフル、水制等)を配備することを妨げな
い。また、上記(6)記載の浄化装置の場合、分割され
た充填槽を個別に処理するので第2の堰に配備される洗
浄水配水管も、ゲ−ト数だけ必要であることは当然のこ
とである。
In order to carry out the river purification method described in (9) more effectively, it does not prevent the fixed and / or movable structure (baffle, water control, etc.) from being provided below the filling tank. Further, in the case of the purifying apparatus described in (6) above, since the divided filling tanks are treated individually, it goes without saying that the number of wash water distribution pipes installed in the second weir is also required. That is.

【0008】[0008]

【発明の実施の形態】本発明の河川の浄化方法及び浄化
装置作用原理を図1に示す。粒径が従来の砕石よりも小
さく比表面積の大きな比重が1に近い浮上性粒子(ポリ
プロピレン、ポリエチレンなどプラスチック粒状物、連
続気泡型ウレタンフォ−ム粒状物など)を隔壁を介して
河川水路または河川敷に設けた水路に充填し、河川水を
自然流下式(ポンプを使わない)で充填層に上向流で流
す。充填層の上部には網などの部材を設け浮上ろ材の流
出を阻止する。
DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 shows the principle of operation of a river purification method and a purification apparatus according to the present invention. Floating particles (plastic granules such as polypropylene and polyethylene, open-cell urethane foam granules, etc.) whose particle size is smaller than that of conventional crushed stones and whose specific surface area is large and whose specific gravity is close to 1 are separated by river walls or river beds through partition walls. It is filled in the water channel provided in, and the river water is allowed to flow upward in the packed bed by a natural flow-down method (no pump is used). A member such as a net is provided above the packed bed to prevent the floating filter medium from flowing out.

【0009】比表面積の大きい浮上性粒子には大量の微
生物が付着しているのでSSの捕捉のみならず高速度で
河川の有機物(BOD)が浄化される。河川の濁質の捕
捉、微生物の増殖により浮上粒子充填層の通水抵抗が増
加するので間欠的に充填層の下部から多量の空気を10
分程度送り込み浮上粒子を攪乱流動させる。その結果そ
れまで浮上粒子に捕捉されていた濁質が剥離される。こ
の剥離濁質を含む水を洗浄排水管から河川水路の外に排
出する。しばらくすると洗浄排水の濁質量が減少してく
るので洗浄排水管の弁を閉じ洗浄排水の排出を止める。
洗浄排水は沈殿槽に流入し、ろ材から除去された汚泥が
沈殿する。沈殿槽は通常河川敷きの陸上に設置する。
Since a large amount of microorganisms are attached to the floating particles having a large specific surface area, the organic matter (BOD) in the river is purified not only by capturing SS but also at a high speed. Because the flow resistance of the floating particle packed bed increases due to the capture of river turbidity and the growth of microorganisms, a large amount of air is intermittently supplied from the bottom of the packed bed 10 times.
The floating particles are disturbed and flowed in for about a minute. As a result, the suspended matter that has been captured by the floating particles is peeled off. The water containing the exfoliated suspended matter is discharged from the cleaning drainage pipe to the outside of the river channel. After a while, the turbid mass of the cleaning drainage decreases, so close the valve of the cleaning drainage pipe to stop the draining of the cleaning drainage.
The washing wastewater flows into the settling tank, and the sludge removed from the filter medium settles. The settling tank is usually installed on the riverside land.

【0010】浮上性固体の比重は0.85以上とするこ
とが重要である。比重がこの値未満であると浮力が大き
すぎ洗浄用空気を供給してもろ材が浮上したままで流動
しないので浮上ろ材の洗浄が行えない。浮上性粒子の粒
径は10mm以下(好ましくは2〜4mm)にし比表面
積を大きくし微生物付着量を高めることが好ましい。河
川の充填層内上向流速は100〜150m/d程度とか
なり大きな流速に設定できる。浮上充填層の層高は河川
の水深以下とし、通常1〜2m程度にする。従って、充
填層の滞留時間は10分程度であり従来より著しく短時
間で浄化できる。微生物呼吸のための散気空気量はBO
D流入負荷量(kg/d)、曝気の酸素吸収効率(8%
程度)から計算して決定する。なお河川のBODが10
mg/l以下と微量な場合は、河川の溶存酸素自体で浄
化できるので微生物呼吸のための曝気は必ずしも必要な
い。
It is important that the specific gravity of the floating solid is 0.85 or more. If the specific gravity is less than this value, the buoyancy is too large, and even if the cleaning air is supplied, the filter medium remains floating and does not flow, so that the floating filter medium cannot be washed. The particle size of the floating particles is preferably 10 mm or less (preferably 2 to 4 mm) to increase the specific surface area and increase the amount of adhering microorganisms. The upward flow velocity in the packed bed of the river can be set to a considerably high flow velocity of about 100 to 150 m / d. The height of the floating packed bed is not more than the depth of the river and is usually about 1 to 2 m. Therefore, the residence time of the packed bed is about 10 minutes, and purification can be performed in a significantly shorter time than in the past. The amount of air diffused for microbial respiration is BO
D inflow load (kg / d), aeration oxygen absorption efficiency (8%
Degree) to determine. The BOD of the river is 10
When the amount is less than mg / l, it can be purified by the dissolved oxygen in the river itself, and aeration for microbial respiration is not always necessary.

【0011】ろ材洗浄のための空気供給量は充填層の空
気線速度を1m/min以上になるように供給する。こ
の空気線速度にすれば浮上ろ材は充分流動し効果的なろ
材洗浄が行える。浮上充填層の隔壁、即ち堰は通常の河
川ならば水流によって流されないように重量の大きなコ
ンクリ−ト製とするのがよいが、本発明の水中構造物を
一体式又は分割式ユニットとして作り、小型水路等に設
置することもよい。浮上ろ材充填層は複数ユニットに分
割し、ろ材洗浄を各ユニットに対して時間をずらして行
うと洗浄排水量が減少できる。このようにすれば洗浄排
水量が安定し、また浄化処理の中断が極力回避される。
洗浄に際しては、ゲ−ト操作を適切に行えば河川水その
ものの圧力を利用して無動力でも行える。洗浄排水処理
のためにの沈殿槽は単なる沈殿槽よりも、空隙率の大き
なろ材(例えば中空円筒ろ材)を充填した槽が沈殿効果
が優れているため好適である。
The air supply amount for cleaning the filter medium is such that the linear air velocity of the packed bed is 1 m / min or more. With this air linear velocity, the floating filter medium flows sufficiently and effective filter medium cleaning can be performed. The partition wall of the floating packed bed, that is, the weir is preferably made of a concrete with a large weight so as not to be washed away by the water flow in a normal river, but the underwater structure of the present invention is formed as an integral type or a split type unit, It may be installed in a small waterway. If the floating filter medium packed bed is divided into a plurality of units and the filter medium cleaning is performed at different times for each unit, the cleaning drainage amount can be reduced. In this way, the amount of cleaning waste water is stabilized, and interruption of the purification process is avoided as much as possible.
When cleaning, if the gate operation is properly performed, the pressure of the river water itself can be used without power. As a sedimentation tank for cleaning wastewater treatment, a tank filled with a filter medium having a large porosity (for example, a hollow cylindrical filter medium) is preferable to a simple sedimentation tank because the sedimentation effect is excellent.

【0012】[0012]

【実施例】以下に実施例により本発明の効果をさらに詳
述する。
EXAMPLES The effects of the present invention will be described in more detail below with reference to examples.

【0013】実施例 汚濁河川を模擬して団地下水の活性汚濁処理水(BOD
10〜15mg/l、SS8〜11mg/l)を対象と
して図1に示すように本発明の試験を行った。試験条件
を以下に示す。 浮上ろ材種類: ポリエチレン粒状物 浮上ろ材粒径: 2〜3 mm 浮上ろ材比重: 0.95 ろ材充填高: 1.5 m 原水流量: 2 l/min 原水上向流速: 200 m/d ろ材洗浄空気流速: 1.5 m/min 充填層滞留時間: 10.8 min ろ材洗浄頻度: 1日に一回 ろ材洗浄時間: 20 min 以上の条件で1年間の通水試験を行った結果、年間を通
して処理水BOD3〜5mg/l、処理水SS1.2〜
2.6mg/lとなり良好な処理水が得られ本発明の汚
濁河川に対する効果が実証できた。なお、ろ材洗浄排水
は粒径25mmのポリプロピレン製中空円筒ろ材を充填
した接触横流沈殿槽に水平流速50m/dで供給したと
ころ沈殿槽流出水水質はBOD4〜5mg/l、SS
2.5〜3.2mg/lであり充分浄化されていた。
Example Simulating a polluted river, activated polluted treated water (BOD)
The test of the present invention was carried out for 10 to 15 mg / l and SS8 to 11 mg / l) as shown in FIG. The test conditions are shown below. Floating filter type: Polyethylene granular material Floating filter particle size: 2-3 mm Floating filter specific gravity: 0.95 Filter medium filling height: 1.5 m Raw water flow rate: 2 l / min Raw water upward velocity: 200 m / d Filter washing air Flow rate: 1.5 m / min Packed bed retention time: 10.8 min Filter media cleaning frequency: Once a day Filter media cleaning time: 20 min As a result of conducting a one-year water flow test under the above conditions, treatment was carried out throughout the year Water BOD3-5 mg / l, treated water SS1.2-
It was 2.6 mg / l, and good treated water was obtained, thus demonstrating the effect of the present invention on a polluted river. The filter medium washing wastewater was supplied at a horizontal flow velocity of 50 m / d to a contact cross-flow sedimentation tank filled with a polypropylene hollow cylindrical filter material having a particle diameter of 25 mm, and the sedimentation tank outflow water quality was BOD 4-5 mg / l, SS.
The amount was 2.5 to 3.2 mg / l, which was sufficiently purified.

【0014】[0014]

【発明の効果】本発明によれば充填層の洗浄が容易であ
るので河川水中のSS及びBODが効率的、連続的に処
理可能であり、またユニット化することにより、浄化装
置の設置が容易となる。
According to the present invention, since the packed bed can be easily washed, SS and BOD in river water can be treated efficiently and continuously, and the unitization makes it easy to install the purification device. Becomes

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

【図1】本発明の河川の浄化方法及び浄化装置の作用原
理図を示す。
FIG. 1 is a diagram showing the principle of operation of a river purification method and a purification apparatus according to the present invention.

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Claims (5)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 河川または水路を横断し、水中に沈没し
て配置した比重が0.85以上1未満の浮上充填剤の充
填層に該河川または水路の水を通過させ、該水中の濁質
及び/または有機物を除去するとともに、前記充填層に
供給する前記水及び/または空気量を増大させて該充填
層を洗浄し、該洗浄排水を該河川または水路の系外に導
いて固液分離した後、分離液は該河川または水路に返送
することを特徴とする河川の浄化方法。
1. Water suspended in a river or waterway is passed through a packed bed of a floating filler having a specific gravity of 0.85 or more and less than 1 which is disposed by being submerged in the water across the river or waterway, and the suspended matter in the water is passed through. And / or organic substances are removed, and the amount of water and / or air supplied to the packed bed is increased to wash the packed bed, and the washing wastewater is guided to the outside of the system of the river or water channel to perform solid-liquid separation. After that, the separated liquid is returned to the river or waterway.
【請求項2】 1)河川または水路を横断する第1の
堰、2)第1の堰の上流側に第1の堰と平行して河川ま
たは水路を横断配置され、且つ下方に開口部を設けた第
2の堰、3)前記両堰の間に沈没配備した比重が0.8
5以上1未満の浮上充填剤の充填層、4)第2の堰の水
面と前記充填層頂端の高さ位置に開口する開閉手段を備
えた洗浄配水管、5)該河川または水路の系外に配置さ
れる該洗浄排水管に連通する固液分離装置、及び6)該
固液分離装置から分離水を該河川または水路に排出する
配管、を備えたことを特徴とする河川の浄化装置。
2. A first weir that crosses a river or a waterway. 2) An upstream side of the first weir is arranged transversely to the river or waterway parallel to the first weir, and an opening is formed below. The second weir provided, 3) The specific gravity of the submerged and deployed weir is 0.8.
5 or more but less than 1 packed bed of floating filler, 4) Washing water distribution pipe equipped with opening / closing means opening at the height of the water surface of the second weir and the top of the packed bed, 5) Outside the system of the river or waterway And a pipe for discharging the separated water from the solid-liquid separation device to the river or the waterway, and a purification device for a river.
【請求項3】 前記第2の堰が下方の開口部に開閉自在
に設けられるゲートを有し、該ゲートが横断方向に複数
に分割され個々に開閉自在に設けられていることを特徴
とする請求項2記載の河川の浄化装置。
3. The second weir has a gate that is openably and closably provided in a lower opening portion, and the gate is divided into a plurality of parts in a transverse direction and individually opened and closably provided. The river purification device according to claim 2.
【請求項4】 前記第2の堰が下方の開口部に開閉自在
に設けられるゲートを有し、前記充填層が該ゲートに対
応して複数に分割され対応するゲートからのみ通水され
ることを特徴とする請求項3記載の河川の浄化装置。
4. The second weir has a gate openably and closably provided in a lower opening, and the filling layer is divided into a plurality of portions corresponding to the gate, and water is passed only from the corresponding gate. The river purification device according to claim 3, wherein
【請求項5】 請求項3記載の河川の浄化装置の充填層
の洗浄に際し、一部のゲートを閉、残りのゲートを開と
して、充填層への通水量および/または通水位置を変化
させることを特徴とする請求項1記載の河川の浄化方
法。
5. When cleaning the packed bed of the river purification apparatus according to claim 3, some of the gates are closed and the remaining gates are opened to change the water flow amount and / or the water flow position to the packed bed. The method for purifying a river according to claim 1, characterized in that.
JP20474595A 1995-08-10 1995-08-10 River purification method and purification device Expired - Fee Related JP3439576B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP20474595A JP3439576B2 (en) 1995-08-10 1995-08-10 River purification method and purification device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP20474595A JP3439576B2 (en) 1995-08-10 1995-08-10 River purification method and purification device

Publications (2)

Publication Number Publication Date
JPH0947770A JPH0947770A (en) 1997-02-18
JP3439576B2 true JP3439576B2 (en) 2003-08-25

Family

ID=16495632

Family Applications (1)

Application Number Title Priority Date Filing Date
JP20474595A Expired - Fee Related JP3439576B2 (en) 1995-08-10 1995-08-10 River purification method and purification device

Country Status (1)

Country Link
JP (1) JP3439576B2 (en)

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