JP7767864B2 - Wastewater treatment method and equipment - Google Patents
Wastewater treatment method and equipmentInfo
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本発明は、排水を凝集及び固液分離処理する排水の処理方法及び装置に係り、特に凝集汚泥の一部を反応槽に返送すると共に、この返送汚泥に消石灰等のアルカリ剤を添加するようにした排水の処理方法及び装置に関する。 The present invention relates to a wastewater treatment method and apparatus that performs coagulation and solid-liquid separation on wastewater, and in particular to a wastewater treatment method and apparatus that returns a portion of the coagulated sludge to a reaction tank and adds an alkaline agent such as slaked lime to this returned sludge.
排水を凝集及び固液分離処理して、濃縮性に富み、脱水性に優れた高濃度汚泥を得る方法として、アルカリ汚泥法等の高密度汚泥法(HDS法:High Density Sludge)が知られている。アルカリ汚泥法では、凝集処理の後段の固液分離処理で分離されて返送される汚泥の一部に消石灰(Ca(OH)2)等のアルカリを添加する。 High Density Sludge (HDS) processes, such as alkaline sludge processes, are known as methods for obtaining high-concentration sludge that is highly thick and has excellent dewaterability by subjecting wastewater to coagulation and solid-liquid separation. In the alkaline sludge process, an alkali such as slaked lime (Ca(OH) 2 ) is added to a portion of the sludge that is separated and returned in the solid-liquid separation process that follows the coagulation process.
図2は、従来の高密度凝集汚泥処理法の代表的な装置を示す系統図であり、原水は原水槽1にてpH調整剤が添加されてpH2.5~3.0程度に調整された後、反応槽2に導入され、後述の改質槽8から導入される改質汚泥と混合され、反応する。この反応液は、次いで凝集槽3に送給され、高分子凝集剤添加手段3aにより高分子凝集剤が添加されて凝集処理された後、沈殿槽4で固液分離される。沈殿槽4の上澄水は処理水として系外へ排出される。沈殿槽4からポンプ5により引き抜かれた分離汚泥の一部は汚泥返送ライン7により改質槽8に返送され、残部は排出ライン6により系外へ排出される。 Figure 2 is a system diagram showing a typical system for a conventional high-density flocculation sludge treatment method. Raw water is adjusted to a pH of approximately 2.5 to 3.0 by the addition of a pH adjuster in raw water tank 1, and then introduced into reaction tank 2, where it is mixed with and reacted with modified sludge introduced from modification tank 8, described below. This reaction liquid is then sent to flocculation tank 3, where a polymer flocculant is added by polymer flocculant addition means 3a for flocculation treatment, and then undergoes solid-liquid separation in settling tank 4. The supernatant water from settling tank 4 is discharged outside the system as treated water. A portion of the separated sludge extracted from settling tank 4 by pump 5 is returned to modification tank 8 via sludge return line 7, and the remainder is discharged outside the system via discharge line 6.
改質槽8では、アルカリ剤添加手段としての消石灰添加手段9により供給される消石灰の溶解/分散液(消石灰の一部は溶解し、残部は分散している液)と返送汚泥とが混合される。この混合液(改質汚泥)は反応槽2に供給される。この反応槽2における反応は所定のpH範囲(例えば6~11、特に6~8)で行うのが好ましく、このようなpH範囲となるように、反応槽2に設けられたpH計2aの検出pHに基づいて改質槽8に供給される消石灰の量が調節される。 In the reforming tank 8, the returned sludge is mixed with a dissolved/dispersed solution of slaked lime (a liquid in which part of the slaked lime is dissolved and the rest is dispersed) supplied by the slaked lime supplying means 9, which acts as an alkaline agent supplying means. This mixed solution (modified sludge) is supplied to the reaction tank 2. The reaction in this reaction tank 2 preferably occurs within a predetermined pH range (e.g., 6 to 11, particularly 6 to 8). The amount of slaked lime supplied to the reforming tank 8 is adjusted based on the pH detected by the pH meter 2a installed in the reaction tank 2 to maintain this pH range.
汚泥排出ライン6及び汚泥返送ライン7にはそれぞれ開閉式のバルブ11,12が設けられている。バルブ11を開、バルブ12を閉とすることにより、ポンプ5からの汚泥の全量が系外に排出される。バルブ12を開、バルブ11を閉とすることにより、ポンプ5からの汚泥の全量が改質槽8に返送される。バルブ11,12の開閉を制御手段(図示略)によって切り替えることにより、改質槽8への汚泥返送量が制御される。 The sludge discharge line 6 and the sludge return line 7 are provided with open/close valves 11 and 12, respectively. By opening valve 11 and closing valve 12, the entire amount of sludge from pump 5 is discharged outside the system. By opening valve 12 and closing valve 11, the entire amount of sludge from pump 5 is returned to the reforming tank 8. The amount of sludge returned to the reforming tank 8 is controlled by switching the opening and closing of valves 11 and 12 using a control means (not shown).
図2に示す従来例において、バルブ11を開とし、バルブ12を閉とし、汚泥の全量を排出ライン6から系外に排出する場合、改質槽8への汚泥返送が無いため、改質槽8から反応槽2への改質汚泥(消石灰添加汚泥)の供給が減少するか又は停止し、反応槽2のpHが所定範囲よりも低くなる。その後、バルブ12を開、バルブ11を閉とし、改質槽8への汚泥返送を再開すると、改質槽8から高pHの改質汚泥が多量に流入し、反応槽2のpHが急激に上昇する。そして、このような急激なpH変動のために、汚泥の改質や凝集が不良となり、処理水質が悪化したり、排出ライン6からの排出汚泥の含水率が高くなったりするおそれがある。 In the conventional example shown in Figure 2, when valve 11 is opened, valve 12 is closed, and the entire amount of sludge is discharged outside the system through discharge line 6, there is no sludge return to the reforming tank 8, so the supply of modified sludge (slaked lime-added sludge) from the reforming tank 8 to the reaction tank 2 is reduced or stopped, and the pH of the reaction tank 2 falls below the specified range. If valve 12 is then opened and valve 11 is closed to resume sludge return to the reforming tank 8, a large amount of high-pH modified sludge flows in from the reforming tank 8, causing the pH of the reaction tank 2 to rise rapidly. Such a sudden pH fluctuation can result in poor sludge modification and coagulation, leading to a deterioration in treated water quality and a high moisture content in the sludge discharged from the discharge line 6.
本発明は、改質槽から反応槽に流入するアルカリ剤添加液の流量を安定化させ、処理水質や排出汚泥性状を常に良好にすることができる排水の処理方法及び装置を提供することを課題とする。 The objective of the present invention is to provide a wastewater treatment method and apparatus that stabilizes the flow rate of alkaline agent-added liquid flowing from the reforming tank to the reaction tank, thereby consistently maintaining good treated water quality and discharged sludge properties.
上記課題を解決するために、本発明の排水の処理方法及び装置は次を要旨とする。 To solve the above problems, the wastewater treatment method and apparatus of the present invention are as follows:
[1] 排水にアルカリ剤添加返送汚泥を添加して反応させ、次いで凝集処理した後、固液分離処理して汚泥を処理水から分離し、
分離した汚泥の一部を返送汚泥とし、この返送汚泥を改質槽に導入して前記アルカリ剤を添加して前記排水に添加し、
汚泥の残部を引き抜き汚泥として排出する排水の処理方法において、
前記改質槽への汚泥返送が停止するか又は汚泥返送量が所定量以下となったときに該改質槽に給水ラインから給水することを特徴とする排水の処理方法。
[1] Adding alkaline agent-added return sludge to wastewater to cause a reaction, then subjecting it to coagulation treatment, and then separating the sludge from the treated water by solid-liquid separation;
A part of the separated sludge is used as return sludge, and this return sludge is introduced into a modification tank, and the alkaline agent is added to the wastewater, and then the returned sludge is added to the modification tank.
In a wastewater treatment method in which the remaining sludge is extracted and discharged as sludge,
A method for treating wastewater, comprising the step of supplying water to the reforming tank from a water supply line when the return of sludge to the reforming tank is stopped or when the amount of sludge returned falls below a predetermined amount.
[2] 前記沈殿槽から前記改質槽への汚泥返送が停止状態のときに前記給水ラインによって前記改質槽に給水する、[1]の排水の処理方法。 [2] The wastewater treatment method of [1], in which water is supplied to the reforming tank through the water supply line when sludge return from the settling tank to the reforming tank is stopped.
[3] 前記改質槽への給水量は、前記汚泥引き抜きを停止しているときの汚泥の返送量と同量である、[2]の排水の処理方法。 [3] The wastewater treatment method of [2], wherein the amount of water supplied to the reforming tank is the same as the amount of sludge returned when sludge extraction is stopped.
[4] 前記水は工業用水である[1]~[3]のいずれかの排水の処理方法。 [4] The wastewater treatment method according to any one of [1] to [3], wherein the water is industrial water.
[5] 排水に改質槽からのアルカリ剤添加返送汚泥を添加する反応槽と、
該反応槽からの液に高分子凝集剤を添加する凝集槽と、
該凝集剤が添加された凝集処理液を固液分離する固液分離手段と、
該固液分離手段で分離された汚泥の一部にアルカリ剤を添加して前記アルカリ剤添加返送汚泥とする改質槽と
を備えてなる排水の処理装置において、
該改質槽に給水可能な給水ラインを設けたことを特徴とする排水の処理装置。
[5] A reaction tank in which alkaline agent-added return sludge from the reforming tank is added to the wastewater;
a coagulation tank for adding a polymer coagulant to the liquid from the reaction tank;
a solid-liquid separation means for separating the flocculation treatment liquid to which the flocculant has been added into solid and liquid;
a modification tank in which an alkaline agent is added to a portion of the sludge separated by the solid-liquid separation means to produce the alkaline agent-added return sludge,
The wastewater treatment device is characterized in that a water supply line capable of supplying water to the reforming tank is provided.
[6] 前記固液分離手段で分離された汚泥を前記改質槽に返送するラインにバルブが設けられており、
該バルブが閉のときに前記給水ラインから前記改質槽に給水を行う給水制御手段を備えた、[5]の排水の処理装置。
[6] A valve is provided on a line for returning the sludge separated by the solid-liquid separation means to the reforming tank,
The wastewater treatment device according to [5], further comprising a water supply control means for supplying water from the water supply line to the reforming tank when the valve is closed.
本発明の排水の処理方法及び装置によると、固液分離手段からの改質槽への汚泥返送量が減少したときでも、改質槽に給水が行われるので、改質槽からアルカリ剤添加液が反応槽に導入されるようになり、反応槽のpHが所定範囲内に保たれる。この結果、凝集が常に良好に行われるようになり、処理水質が良好になると共に、汚泥含水率も低いものとなる。 With the wastewater treatment method and apparatus of the present invention, even when the amount of sludge returned from the solid-liquid separation means to the reforming tank decreases, water is still supplied to the reforming tank, allowing alkaline agent-added liquid to be introduced from the reforming tank into the reaction tank, maintaining the pH of the reaction tank within a specified range. As a result, coagulation is always performed well, improving the quality of the treated water and reducing the water content of the sludge.
以下、図面を参照して実施の形態について説明する。図1は本発明の実施の形態に係る排水の処理方法が適用された排水処理設備のフロー図である。なお、図2と同一部分には同一符号を付してある。 Embodiments will now be described with reference to the drawings. Figure 1 is a flow diagram of a wastewater treatment facility to which a wastewater treatment method according to an embodiment of the present invention is applied. Note that parts that are the same as those in Figure 2 are assigned the same reference numerals.
この実施の形態においても、図2と同様に、原水は原水槽1にてpH調整剤が添加されてpH2.5~3.0程度に調整された後、反応槽2に導入され、改質槽8から導入される改質汚泥と混合され、反応する。この反応液は、次いで凝集槽3に送給され、高分子凝集剤添加手段3aにより高分子凝集剤が添加されて凝集処理された後、沈殿槽4で固液分離される。沈殿槽4の上澄水は処理水として系外へ排出される。沈殿槽4からポンプ5により引き抜かれた分離汚泥の一部は汚泥返送ライン7により改質槽8に返送され、残部は排出ライン6により系外へ排出される。 In this embodiment, as in Figure 2, raw water is adjusted to a pH of approximately 2.5 to 3.0 by the addition of a pH adjuster in raw water tank 1, and then introduced into reaction tank 2, where it is mixed with and reacted with modified sludge introduced from modification tank 8. This reaction liquid is then sent to coagulation tank 3, where a polymer coagulant is added by polymer coagulant addition means 3a for coagulation treatment, and then undergoes solid-liquid separation in settling tank 4. The supernatant water from settling tank 4 is discharged outside the system as treated water. A portion of the separated sludge extracted from settling tank 4 by pump 5 is returned to modification tank 8 via sludge return line 7, and the remainder is discharged outside the system via discharge line 6.
改質槽8では、アルカリ剤添加手段としての消石灰添加手段9により供給される消石灰の溶解/分散液と返送汚泥とが混合される。この混合液(改質汚泥)は反応槽2に供給される。この反応槽2における反応は所定のpH範囲(例6~11、特に6~8)で行うのが好ましく、このようなpH範囲となるように、反応槽2に設けられたpH計2aの検出pHに基づいて改質槽8に供給される消石灰の量が調節される。 In the reforming tank 8, a dissolved/dispersed solution of slaked lime supplied by the slaked lime supplying means 9, which serves as an alkaline agent supplying means, is mixed with the returned sludge. This mixture (modified sludge) is supplied to the reaction tank 2. The reaction in this reaction tank 2 preferably occurs within a predetermined pH range (e.g., 6 to 11, particularly 6 to 8). The amount of slaked lime supplied to the reforming tank 8 is adjusted based on the pH detected by the pH meter 2a installed in the reaction tank 2 to maintain this pH range.
汚泥排出ライン6及び汚泥返送ライン7にはそれぞれ開閉式のバルブ11,12が設けられている。バルブ11を開、バルブ12を閉とすることにより、ポンプ5からの汚泥の全量が系外に排出される。バルブ12を開、バルブ11を閉とすることにより、ポンプ5からの汚泥の全量が改質槽8に返送される。バルブ11,12の開閉を制御手段(図示略)によって切り替えることにより、改質槽8への汚泥返送量が制御される。 The sludge discharge line 6 and the sludge return line 7 are provided with open/close valves 11 and 12, respectively. By opening valve 11 and closing valve 12, the entire amount of sludge from pump 5 is discharged outside the system. By opening valve 12 and closing valve 11, the entire amount of sludge from pump 5 is returned to the reforming tank 8. The amount of sludge returned to the reforming tank 8 is controlled by switching the opening and closing of valves 11 and 12 using a control means (not shown).
この実施の形態においては、改質槽8に水を供給するための給水ライン14が設けられており、該給水ライン14にバルブ13が設けられている。バルブ13は開閉式のバルブであってもよく、流量調節可能な流量調節バルブであってもよい。 In this embodiment, a water supply line 14 is provided to supply water to the reforming tank 8, and a valve 13 is provided on the water supply line 14. The valve 13 may be an open/close valve or a flow control valve that can adjust the flow rate.
このバルブ13は、制御手段(図示略)により、バルブ11が開でバルブ12が閉の状態のときに開とされる。また、バルブ12が開でバルブ11が閉のときには、バルブ13は閉とされる。 This valve 13 is opened by a control means (not shown) when valve 11 is open and valve 12 is closed. Also, when valve 12 is open and valve 11 is closed, valve 13 is closed.
給水ライン14から給水する水としては、工業用水、井水、市水、河川水、排水処理法流水などが例示されるが、中でも工業用水が好適である。 Examples of water supplied from the water supply line 14 include industrial water, well water, city water, river water, and wastewater treatment plant runoff, with industrial water being particularly preferred.
バルブ12閉のときにバルブ13を開として改質槽8に給水しているときの給水量は、バルブ12開のときの返送汚泥量と同量となるように設定することが好ましい。 When valve 12 is closed and valve 13 is opened to supply water to the reforming tank 8, it is preferable to set the amount of water supplied to be the same as the amount of sludge returned when valve 12 is open.
このように、この実施の形態では、沈殿槽4からの改質槽8への汚泥返送が停止しているときには、給水ライン14によって改質槽8に水が供給されるので、改質槽8から反応槽2にアルカリ性の消石灰含有液が導入される。このため、反応槽2内のpHが常に所定範囲(好ましくは6~11、特に好ましくは6~8)に保たれ、凝集反応が十分に行われ、処理水質が良好になると共に、排出ライン6から排出される凝集汚泥の水分含有率が低いものとなる。 In this embodiment, when the return of sludge from the settling tank 4 to the reforming tank 8 is stopped, water is supplied to the reforming tank 8 via the water supply line 14, and alkaline slaked lime-containing liquid is introduced from the reforming tank 8 to the reaction tank 2. As a result, the pH in the reaction tank 2 is always maintained within a predetermined range (preferably 6 to 11, and particularly preferably 6 to 8), the coagulation reaction proceeds sufficiently, the treated water quality is improved, and the water content of the coagulated sludge discharged from the discharge line 6 is low.
本発明で処理対象とする原水としては、フッ素含有排水、リン含有排水、鉄、亜鉛、銅、クロム、ニッケル、鉛、アルミなどの重金属含有排水などが例示されるが、これらに限定されない。 Examples of raw water to be treated by the present invention include, but are not limited to, fluorine-containing wastewater, phosphorus-containing wastewater, and wastewater containing heavy metals such as iron, zinc, copper, chromium, nickel, lead, and aluminum.
上記実施の形態では、改質槽8にアルカリ剤として消石灰を添加しているが、これに限定されるものではなく、重金属含有排水の場合、苛性ソーダなどであってもよい。 In the above embodiment, slaked lime is added to the reforming tank 8 as an alkaline agent, but this is not limited to this. In the case of wastewater containing heavy metals, caustic soda or the like may also be used.
上記実施の形態は本発明の一例であり、本発明は上記以外の態様とされてもよい。例えば、バルブ12,13を流量調節可能なものとし、改質槽8への汚泥返送量を増減調節可能とすると共に、改質槽8への汚泥返送量がバルブ12全開時の汚泥返送量よりも少なくなるほど改質槽8への給水ライン14からの給水量を多くするようにしてもよい。 The above embodiment is one example of the present invention, and the present invention may be embodied in other forms. For example, valves 12 and 13 may be designed to be flow-adjustable, allowing the amount of sludge returned to the reforming tank 8 to be adjusted to an increased or decreased amount, and the amount of water supplied to the reforming tank 8 from the water supply line 14 may be increased so that the amount of sludge returned to the reforming tank 8 becomes less than the amount of sludge returned when valve 12 is fully open.
2 反応槽
3 凝集反応槽
4 沈殿槽
8 改質槽
9 消石灰添加手段
14 給水ライン
2 Reaction tank 3 Coagulation reaction tank 4 Sedimentation tank 8 Modification tank 9 Slaked lime adding means 14 Water supply line
Claims (5)
分離した汚泥の一部を返送汚泥とし、この返送汚泥を改質槽に導入してアルカリ剤を添加して前記アルカリ剤添加返送汚泥として前記排水に添加し、
汚泥の残部を引き抜き汚泥として排出する排水の処理方法において、
前記改質槽への汚泥返送が停止するか又は汚泥返送量が所定量以下となったときに該改質槽に給水ラインから給水することを特徴とする排水の処理方法。 The alkaline agent-added return sludge is added to the wastewater to cause a reaction, followed by coagulation treatment, followed by solid-liquid separation treatment in a settling tank to separate the sludge from the treated water,
A part of the separated sludge is used as return sludge, and this return sludge is introduced into a modification tank , an alkaline agent is added, and the alkaline agent-added return sludge is added to the wastewater;
In a wastewater treatment method in which the remaining sludge is extracted and discharged as sludge,
A method for treating wastewater, comprising the step of supplying water to the reforming tank from a water supply line when the return of sludge to the reforming tank is stopped or when the amount of sludge returned falls below a predetermined amount.
該反応槽からの液に高分子凝集剤を添加する凝集槽と、
該凝集剤が添加された凝集処理液を固液分離する固液分離手段と、
該固液分離手段で分離された汚泥の一部にアルカリ剤を添加して前記アルカリ剤添加返送汚泥とする改質槽と
を備えてなる排水の処理装置において、
該改質槽に給水可能な給水ラインを設けた排水の処理装置であって、
前記固液分離手段で分離された汚泥を前記改質槽に返送するラインにバルブが設けられており、
該バルブが閉のときに前記給水ラインから前記改質槽に給水を行う給水制御手段を備えたことを特徴とする排水の処理装置。 a reaction tank in which the alkaline agent-added return sludge from the reforming tank is added to the wastewater;
a coagulation tank for adding a polymer coagulant to the liquid from the reaction tank;
a solid-liquid separation means for separating the flocculation treatment liquid to which the flocculant has been added into solid and liquid;
a modification tank in which an alkaline agent is added to a portion of the sludge separated by the solid-liquid separation means to produce the alkaline agent-added return sludge,
A wastewater treatment device provided with a water supply line capable of supplying water to the reforming tank,
a valve is provided in a line for returning the sludge separated by the solid-liquid separation means to the reforming tank;
a water supply control means for supplying water from the water supply line to the reforming tank when the valve is closed ;
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Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2001054791A (en) | 1999-08-19 | 2001-02-27 | Kurita Water Ind Ltd | Wastewater treatment equipment |
| JP2001276848A (en) | 2000-03-29 | 2001-10-09 | Kurita Water Ind Ltd | Water treatment equipment |
| JP2003071469A (en) | 2001-09-06 | 2003-03-11 | Kurita Water Ind Ltd | Fluorine-containing water treatment method |
| WO2015198438A1 (en) | 2014-06-26 | 2015-12-30 | 栗田工業株式会社 | Method and device for treating fluoride-containing water |
| JP2018079439A (en) | 2016-11-17 | 2018-05-24 | 栗田工業株式会社 | Method and apparatus for treating wastewater containing sulfuric acid, fluorine and heavy metal ions |
| CN212269679U (en) | 2020-03-19 | 2021-01-01 | 中国电子系统工程第二建设有限公司 | Complete equipment for modifying and efficiently settling fluorine-containing wastewater sludge |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| JP3348636B2 (en) * | 1997-10-06 | 2002-11-20 | 栗田工業株式会社 | Water treatment equipment containing inorganic pollutants |
| JP4867269B2 (en) * | 2005-10-06 | 2012-02-01 | 栗田工業株式会社 | Method and apparatus for treating fluorine-containing water |
| KR20070039723A (en) * | 2005-10-10 | 2007-04-13 | 삼성전자주식회사 | Fluorine Wastewater Treatment System and Fluorine Wastewater Treatment Method |
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Patent Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2001054791A (en) | 1999-08-19 | 2001-02-27 | Kurita Water Ind Ltd | Wastewater treatment equipment |
| JP2001276848A (en) | 2000-03-29 | 2001-10-09 | Kurita Water Ind Ltd | Water treatment equipment |
| JP2003071469A (en) | 2001-09-06 | 2003-03-11 | Kurita Water Ind Ltd | Fluorine-containing water treatment method |
| WO2015198438A1 (en) | 2014-06-26 | 2015-12-30 | 栗田工業株式会社 | Method and device for treating fluoride-containing water |
| JP2018079439A (en) | 2016-11-17 | 2018-05-24 | 栗田工業株式会社 | Method and apparatus for treating wastewater containing sulfuric acid, fluorine and heavy metal ions |
| CN212269679U (en) | 2020-03-19 | 2021-01-01 | 中国电子系统工程第二建设有限公司 | Complete equipment for modifying and efficiently settling fluorine-containing wastewater sludge |
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