JP2007117984A - Apparatus for treating heavy metals-containing water - Google Patents

Apparatus for treating heavy metals-containing water Download PDF

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JP2007117984A
JP2007117984A JP2005373333A JP2005373333A JP2007117984A JP 2007117984 A JP2007117984 A JP 2007117984A JP 2005373333 A JP2005373333 A JP 2005373333A JP 2005373333 A JP2005373333 A JP 2005373333A JP 2007117984 A JP2007117984 A JP 2007117984A
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tank
reaction tank
solid
containing water
liquid separation
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Hiroshi Hayashi
浩志 林
Hitoshi Takeuchi
均 竹内
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Mitsubishi Materials Corp
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<P>PROBLEM TO BE SOLVED: To provide a treatment apparatus for removing heavy metals from drainage efficiently and economically. <P>SOLUTION: In the treatment apparatus having a reactor for mixing heavy metals-containing water with a reducing iron compound to generate a precipitation and a tank for carrying out solid-liquid separation of slurry removed from the reactor, the apparatus for treating the heavy metals-containing water comprises means for providing at least one of the above reactor and the solid-liquid separation tank with a variable magnetic field, accelerating precipitation formation while varying a magnetic field in the reactor and accelerating solid-liquid separation while varying a magnetic field in the solid-liquid separation tank. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は、重金属類を含む排水等から効率よく重金属類を除去する経済性に優れた処理装置に関する。より詳しくは、工程が簡単で実用性に優れ、常温で効率よく排水等に含まれる重金属類を除去する経済性に優れた重金属類含有水の処理装置に関する。 The present invention relates to an economical processing apparatus that efficiently removes heavy metals from wastewater containing heavy metals. More specifically, the present invention relates to an apparatus for treating heavy metal-containing water that is simple in process, excellent in practicality, and efficient in removing heavy metals contained in wastewater and the like efficiently at room temperature.

排水等に含まれる重金属類を沈殿化しまたは凝集して除去する処理方法が従来から多数知られており、重金属類凝集体または重金属類沈殿を効率よく分離する手段として磁気分離手段が知られている。特許文献1には、廃液中の重金属類イオンを凝集する手段と超電導ソレノイド磁石によって強磁場を形成して廃液中の粒子を捕獲する磁気フィルターを用いる分離手段が記載されている。 Many treatment methods for precipitating or agglomerating and removing heavy metals contained in waste water and the like have been known, and magnetic separation means are known as means for efficiently separating heavy metal aggregates or heavy metal precipitates. . Patent Document 1 describes a means for aggregating heavy metal ions in the waste liquid and a separation means using a magnetic filter that captures particles in the waste liquid by forming a strong magnetic field with a superconducting solenoid magnet.

また特許文献2には、重金属類排水に第一鉄イオンを添加してフェライト汚泥を形成し、これをシックナーまたは磁気分離機などで分離する処理方法が記載されている。さらに、特許文献3には、凝集沈殿法やフェライト法によって燐や重金属類を凝集ないし沈殿化する際に、マグネタイト粒子等を添加して磁性を強化した凝集体を形成し、これを磁気分離する処理方法が記載されている。
特開2000−117142号公報 特開2001−321781号公報 特開2001−259657号公報
Patent Document 2 describes a processing method in which ferrous ions are added to heavy metal wastewater to form ferrite sludge, which is separated by a thickener or a magnetic separator. Further, in Patent Document 3, when phosphorus or heavy metals are aggregated or precipitated by the aggregation precipitation method or the ferrite method, an aggregate having enhanced magnetism is formed by adding magnetite particles or the like, and this is magnetically separated. A processing method is described.
JP 2000-117142 A Japanese Patent Laid-Open No. 2001-321781 JP 2001-259657 A

従来の上記処理方法において採用されている磁気分離は、何れも磁場を静的に与えるものであり、磁気分離効果には限界がある。とくに排水等に含まれる重金属類を沈殿化したものは重金属類の種類や沈殿状態によって多種多様であり、固定的な磁場を静的に与えるだけでは十分な分離効果が得られないと云う問題がある。 Any of the magnetic separations employed in the above-described conventional processing methods statically applies a magnetic field, and there is a limit to the magnetic separation effect. In particular, sedimentation of heavy metals contained in wastewater, etc., varies depending on the type of heavy metals and the state of sedimentation, and there is a problem that sufficient separation effects cannot be obtained simply by statically applying a fixed magnetic field. is there.

本発明は、排水等に含まれる重金属類を沈殿化して濾過分離する処理装置において、従来の上記課題を解決したものであり、重金属類を沈殿化する反応槽、または沈殿を分離する固液分離槽の何れかまたは両方に変動磁場を与えることによって、重金属類の沈殿化を促進し、あるいは固液分離効果を高めることができる処理装置を提供するものである。 The present invention solves the above-mentioned conventional problems in a processing apparatus for precipitating and separating heavy metals contained in waste water and the like, and is a reaction tank for precipitating heavy metals, or solid-liquid separation for separating the precipitates It is an object of the present invention to provide a processing apparatus that can accelerate precipitation of heavy metals or enhance a solid-liquid separation effect by applying a varying magnetic field to either or both of the tanks.

本発明によれば以下の構成からなる処理装置が提供される。
(1)重金属類含有水と還元性鉄化合物とを混合して沈殿を生じさせる反応槽、該反応槽から抜き出したスラリーを固液分離する槽を有する処理装置において、上記反応槽または固液分離槽の少なくとも何れかに変動磁場を与える手段を有しており、反応槽において磁場を変動させながら沈澱生成を促し、または固液分離槽において磁場を変動させなら固液分離を促すことを特徴とする重金属類含有水の処理装置。
(2)上記(1)の処理装置において、重金属類含有水と還元性鉄化合物とを混合して沈澱を生じさせる密閉型反応槽を有し、該反応槽から抜き出したスラリーを固液分離する槽、分離した沈殿物(汚泥)の一部または全部にアルカリを添加する槽、アルカリ化した汚泥を上記密閉反応槽に返送する管路を有し、該密閉反応槽において、非酸化性雰囲気下、アルカリ性下で還元性の鉄化合物沈澱を生成する一方、密閉反応槽からスラリーを抜き出してアルカリ添加を経て再び密閉反応槽に返送する循環経路の何れかの工程において上記スラリーないし汚泥と空気との接触を調整して鉄化合物の酸化を抑制し、上記各工程を繰り返して重金属類含有水を処理する装置において、上記反応槽または固液分離槽の少なくとも何れかに変動磁場を与える手段を有する重金属類含有水の処理装置。
(3)反応槽の周囲または固液分離槽の隔壁に磁石を配設し、該磁石を回転または振動させることによって、該磁石によって形成される磁場を変動させる上記(1)または上記(2)に記載する排水の処理装置。
(4)反応槽の周囲または固液分離槽の隔壁に電磁石を配設し、該電磁石の電流を制御することによって、該電磁石によって形成される磁場を変動させる上記(1)または上記(2)に記載する排水の処理装置。
(5)上記(1)〜(4)の何れかの処理装置において、重金属類含有水と還元性鉄化合物とを混合反応させる反応槽の前に、重金属類含有水に還元性鉄化合物を添加する槽を有する重金属類含有水の処理装置。
(6)上記(1)〜(5)の何れかの処理装置において、重金属類含有水に還元性鉄化合物を添加する槽の前に、重金属類含有水に鉄化合物またはアルミニウム化合物を添加する槽、および生成した沈澱を固液分離する槽が設けられている重金属類含有水の処理装置。
(7)上記(1)〜(6)の何れかの処理装置において、複数の反応槽が直列に設けられており、任意の反応槽およびまたは固液分離槽に変動磁場を与える手段が設けられている重金属類含有水の処理装置。
(8)上記(1)〜(7)の何れかの処理装置において、反応槽の上部が蓋材で覆われており、該蓋材は攪拌機の軸部材が挿通する小孔を有し、かつ該蓋は上記小孔に向かって上向きの傾斜を有しており、反応槽内部は上記小孔を通じて外気との連通が制限されて非酸化性雰囲気に保たれている重金属類含有水の処理装置。
According to the present invention, a processing apparatus having the following configuration is provided.
(1) In a processing apparatus having a reaction vessel in which heavy metal-containing water and a reducing iron compound are mixed to cause precipitation, and a vessel for solid-liquid separation of the slurry extracted from the reaction vessel, the reaction vessel or the solid-liquid separation. It has means for applying a variable magnetic field to at least one of the tanks, and promotes precipitation generation while changing the magnetic field in the reaction tank, or promotes solid-liquid separation if the magnetic field is changed in the solid-liquid separation tank. Equipment for water containing heavy metals.
(2) In the processing apparatus of (1), the apparatus has a sealed reaction tank that causes precipitation by mixing heavy metal-containing water and a reducing iron compound, and the slurry extracted from the reaction tank is subjected to solid-liquid separation. A tank, a tank for adding alkali to a part or all of the separated precipitate (sludge), and a pipe for returning the alkalinized sludge to the sealed reaction tank, in a non-oxidizing atmosphere in the sealed reaction tank , While producing a reductive iron compound precipitate under alkalinity, the slurry or sludge and the air in any step of the circulation path where the slurry is withdrawn from the sealed reaction tank and returned to the sealed reaction tank through alkali addition. In a device that adjusts contact to suppress oxidation of the iron compound and repeats the above steps to treat heavy metal-containing water, a variable magnetic field is applied to at least one of the reaction tank and the solid-liquid separation tank. Processor of heavy metals-containing water having a stage.
(3) The above-described (1) or (2) above, wherein a magnet is disposed around the reaction tank or in the partition wall of the solid-liquid separation tank, and the magnetic field formed by the magnet is changed by rotating or vibrating the magnet. Wastewater treatment equipment described in 1.
(4) The above-described (1) or (2) above, wherein an electromagnet is disposed around the reaction tank or in the partition wall of the solid-liquid separation tank, and the electric field generated by the electromagnet is controlled by controlling the current of the electromagnet. Wastewater treatment equipment described in 1.
(5) In the processing apparatus according to any one of (1) to (4) above, the reducing iron compound is added to the heavy metal-containing water before the reaction vessel in which the heavy metal-containing water and the reducing iron compound are mixed and reacted. An apparatus for treating heavy metal-containing water having a tank to be used.
(6) In the processing apparatus according to any one of (1) to (5) above, a tank for adding an iron compound or an aluminum compound to the heavy metal-containing water before the tank for adding the reducing iron compound to the heavy metal-containing water And a heavy metal-containing water treatment apparatus provided with a tank for solid-liquid separation of the generated precipitate.
(7) In the processing apparatus of any one of (1) to (6) above, a plurality of reaction vessels are provided in series, and a means for applying a variable magnetic field to any reaction vessel and / or solid-liquid separation vessel is provided. Equipment for water containing heavy metals.
(8) In the processing apparatus according to any one of (1) to (7), the upper part of the reaction tank is covered with a cover material, the cover material has a small hole through which a shaft member of a stirrer is inserted, and The treatment apparatus for treating heavy metal-containing water in which the lid has an upward slope toward the small hole and the inside of the reaction tank is maintained in a non-oxidizing atmosphere with limited communication with outside air through the small hole .

本発明の処理装置は、重金属類含有水に還元性鉄化合物を添加して重金属類を沈澱化し、この沈澱を固液分離して重金属類を除去する処理装置において、重金属類を沈殿化する反応槽または沈殿を分離する固液分離槽の少なくとも何れかに変動磁場を与える手段を有し、磁場を変動させながら重金属類の沈澱化を促し、または重金属類沈澱の分離を促するので、重金属類除去効果を高めることができる。 The treatment apparatus of the present invention is a reaction for precipitating heavy metals in a treatment apparatus for adding heavy irons to water containing heavy metals to precipitate heavy metals and then separating the precipitates into solid and liquid to remove heavy metals. A means for applying a variable magnetic field to at least one of the tank and the solid-liquid separation tank for separating the precipitate, and promotes precipitation of heavy metals while fluctuating the magnetic field, or promotes separation of precipitation of heavy metals. The removal effect can be enhanced.

また、本発明の処理装置において、分離した汚泥の一部または全部にアルカリを添加してアルカリ化した汚泥を反応槽に返送する循環系を有するものは、該反応槽において、非酸化性雰囲気下、アルカリ性下で反応させて還元性の鉄化合物沈澱を生成するので、常温で鉄フェライト化を進めることができ、圧密されたコンパクトな澱物を形成するので脱水性が良く、かつ重金属類の除去効果も高い。 Further, in the treatment apparatus of the present invention, an apparatus having a circulation system for returning alkalinized sludge by adding alkali to a part or all of the separated sludge is a non-oxidizing atmosphere in the reaction tank. , Reacting under alkaline conditions to produce a reductive iron compound precipitate, so that iron ferritization can proceed at room temperature, forming compacted and compact starch, good dehydration, and removal of heavy metals The effect is also high.

さらに、本発明の処理装置において、重金属類含有水に、あらかじめ鉄化合物またはアルミニウム化合物を添加するものは、この前処理によってケイ酸イオン、アルミニウムイオン、微量有機物などのフェライト化の阻害原因が予め除去されるので、処理効果をさらに高めることができる。 Furthermore, in the treatment apparatus of the present invention, in the case where an iron compound or an aluminum compound is added in advance to heavy metal-containing water, this pretreatment removes in advance the cause of inhibition of ferritization such as silicate ions, aluminum ions, and trace organic substances. Therefore, the processing effect can be further enhanced.

本発明の処理装置は、重金属類含有水と還元性鉄化合物とを混合して沈殿を生じさせる反応槽、該反応槽から抜き出したスラリーを固液分離する槽を有する処理装置において、上記反応槽または固液分離槽の少なくとも何れかに変動磁場を与える手段を有しており、反応槽において磁場を変動させながら沈澱生成を促し、または固液分離槽において磁場を変動させなら固液分離を促すことを特徴とする重金属類含有水の処理装置である。 The processing apparatus of the present invention is a processing apparatus comprising: a reaction tank that mixes heavy metal-containing water and a reducing iron compound to cause precipitation; and a tank that solid-liquid separates a slurry extracted from the reaction tank. Alternatively, it has means for applying a varying magnetic field to at least one of the solid-liquid separation tanks, and promotes precipitation generation while changing the magnetic field in the reaction tank, or promotes solid-liquid separation if the magnetic field is changed in the solid-liquid separation tank. It is the processing apparatus of the heavy metal containing water characterized by the above-mentioned.

本発明の処理装置は、好ましくは、重金属類含有水と還元性鉄化合物とを混合して沈澱を生じさせる密閉型反応槽を有し、該反応槽から抜き出したスラリーを固液分離する槽、分離した沈殿物(汚泥)の一部または全部にアルカリを添加する槽、アルカリ化した汚泥を上記密閉反応槽に返送する管路を有し、該密閉反応槽において、非酸化性雰囲気下、アルカリ性下で還元性の鉄化合物沈澱を生成する一方、密閉反応槽からスラリーを抜き出してアルカリ添加を経て再び密閉反応槽に返送する循環経路の何れかの工程において上記スラリーないし汚泥と空気との接触を調整して鉄化合物の酸化を抑制し、上記各工程を繰り返して重金属類含有水を処理する装置において、上記反応槽または固液分離槽の少なくとも何れかに変動磁場を与える手段を有する重金属類含有水の処理装置である。 The treatment apparatus of the present invention preferably has a sealed reaction tank that causes precipitation by mixing heavy metal-containing water and a reducing iron compound, and a tank for solid-liquid separation of the slurry extracted from the reaction tank, A tank for adding alkali to a part or all of the separated sediment (sludge), a pipe for returning the alkalinized sludge to the sealed reaction tank, and in the sealed reaction tank, alkaline in a non-oxidizing atmosphere The reductive iron compound precipitate is generated under the condition, while the slurry or sludge is brought into contact with the air in any step of the circulation path in which the slurry is extracted from the sealed reaction tank and returned to the sealed reaction tank through alkali addition. In a device that adjusts to suppress oxidation of the iron compound and repeats the above steps to treat heavy metal-containing water, a method of applying a varying magnetic field to at least one of the reaction tank and the solid-liquid separation tank A processing apparatus of heavy metals containing water have.

本発明に係る処理装置の一例を図1、図2に示す。図1は分離した汚泥の一部または全部にアルカリを添加してアルカリ化した汚泥を反応槽に返送する循環系を有する装置例であり、図2は前処理工程を有する装置例である。 An example of the processing apparatus according to the present invention is shown in FIGS. FIG. 1 is an example of an apparatus having a circulation system that returns alkali to a reaction tank by adding alkali to a part or all of the separated sludge, and FIG. 2 is an example of an apparatus having a pretreatment step.

図1の処理装置は、重金属類含有水に還元性鉄化合物を添加する槽10、還元性鉄化合物と重金属類を反応させて沈殿を生成させる非酸化性雰囲気の密閉反応槽30、該反応槽30から抜き出したスラリーを固液分離する槽40、分離した汚泥(沈殿物)にアルカリを添加する槽20、アルカリ性汚泥を反応槽30に返送する管路、これらの各槽を連通する管路を備えており、上記反応槽30または固液分離槽40の少なくとも何れかに変動磁場を与える手段50が設けられている。 1 includes a tank 10 for adding a reducing iron compound to heavy metal-containing water, a closed reaction tank 30 in a non-oxidizing atmosphere that reacts the reducing iron compound with heavy metals to form a precipitate, and the reaction tank. A tank 40 for solid-liquid separation of the slurry extracted from 30, a tank 20 for adding alkali to the separated sludge (precipitate), a pipe for returning alkaline sludge to the reaction tank 30, and a pipe for connecting these tanks A means 50 for providing a varying magnetic field to at least one of the reaction tank 30 and the solid-liquid separation tank 40 is provided.

変動磁場を与える手段50は、例えば、反応槽30の外周に回転自在な支持枠(図示省略)を設け、該支持枠に該反応槽30を囲むように磁石(図示省略)を設けることによって該反応槽内部を含む磁場を形成、上記支持枠を回転することによって上記磁場を回転変動させる構造などによって形成することができる。あるいは回転自在な支持枠に代えて上下振動する支持枠を用い、磁石を装着した支持枠を上下動させて、上記磁場を上下振動させる構造でもよい。また、複数の電磁石を用い、電磁石への通電を切り替えて電気的に磁場を変動する構成でもよい。反応槽内ではフェライト化が進行し、磁性を帯びた沈殿が形成されるので、変動磁場を与えることによって、このフェライト化がさらに促進される。 The means 50 for applying a varying magnetic field is provided, for example, by providing a rotatable support frame (not shown) on the outer periphery of the reaction vessel 30 and providing a magnet (not shown) around the reaction vessel 30 on the support frame. A magnetic field including the inside of the reaction vessel can be formed, and a structure in which the magnetic field is rotationally changed by rotating the support frame can be formed. Alternatively, a structure in which a support frame that vibrates up and down is used instead of a rotatable support frame and the support frame on which the magnet is mounted is moved up and down to vibrate the magnetic field up and down may be used. Moreover, the structure which changes a magnetic field electrically by switching the electricity supply to an electromagnet using a some electromagnet may be sufficient. Ferritization proceeds in the reaction tank, and a magnetic precipitate is formed. Therefore, the ferrite formation is further promoted by applying a variable magnetic field.

また、固液分離槽40の磁場変動手段50は、上記構造の他に、例えば、槽内に中央部を囲む支持枠(図示省略)を立設し、該支持枠に電磁石などを設け、該電磁石への通電を切り替えることによって、断続的に磁場を形成することによって磁場を変動させてもよい。磁場を形成することによって磁性を帯びた沈殿の凝集が進み、磁場を消すことによって凝集体の沈降が促される。 In addition to the above structure, the magnetic field changing means 50 of the solid-liquid separation tank 40 is provided with, for example, a support frame (not shown) surrounding the central portion in the tank, and an electromagnet or the like provided on the support frame. The magnetic field may be changed by intermittently forming the magnetic field by switching the energization to the electromagnet. By forming a magnetic field, the precipitation of the magnetic precipitate proceeds, and by turning off the magnetic field, the sedimentation of the aggregate is promoted.

電磁石を用いた磁場変動の例を図3〜図6に示す。図3に示すように、シックナー82の外周に複数の電磁石81が装着されている。複数の電磁石81は図4に示すようにシックナー82の底部に設けても良い。これらの電磁石81は制御部80に接続されており、該制御部80によって各電磁石81の電流が制御される。 Examples of magnetic field fluctuations using electromagnets are shown in FIGS. As shown in FIG. 3, a plurality of electromagnets 81 are mounted on the outer periphery of the thickener 82. The plurality of electromagnets 81 may be provided at the bottom of the thickener 82 as shown in FIG. These electromagnets 81 are connected to the control unit 80, and the current of each electromagnet 81 is controlled by the control unit 80.

スラリーの導入によってシックナー82の内部には図示するような対流が生じ、微細な澱物粒子が槽壁に沿って浮上し、懸濁物となり、オーバフローとなって系外に流出するようになる。このような澱物粒子の流出を防止するために、電磁石に通電してシックナーを含む範囲に磁場を形成して澱物粒子の浮遊を抑制する。澱物粒子はフェライト質であるので、磁場の形成によってシックナー壁面に引き寄せられ、該壁面に付着するようになる。所定時間後に電磁石の通電を止めて磁場を解消すると、シックナー壁面に付着していた澱物粒子は磁力の消失によってシックナー底部に沈降し、排出口を通じて系外に排出される。図4に示す構造の場合にも同様であり、磁場の形成によって澱物粒子がシックナー底部に集まり、磁場を解消することによって排出口から系外に排出される。 By introducing the slurry, convection as shown in the figure is generated inside the thickener 82, and fine starch particles float along the tank wall, become suspended, overflow, and flow out of the system. In order to prevent such outflow of starch particles, the electromagnet is energized to form a magnetic field in the range including the thickener, thereby suppressing the starch particles from floating. Since the starch particles are ferritic, they are attracted to the wall surface of the thickener by the formation of a magnetic field and adhere to the wall surface. When the energization of the electromagnet is stopped after a predetermined time and the magnetic field is eliminated, the starch particles adhering to the thickener wall surface settle to the bottom of the thickener due to the disappearance of the magnetic force and are discharged out of the system through the discharge port. The same applies to the structure shown in FIG. 4. The starch particles gather at the bottom of the thickener by the formation of the magnetic field, and are discharged out of the system from the discharge port by eliminating the magnetic field.

図5および図6は反応槽(反応容器)90に電磁石81を取り付けた例である。図示するように、反応容器90の槽壁に複数の電磁石81が等間隔で取付られており、各電磁石は制御部(図示省略)に接続されている。各電磁石81の電流は制御部によって制御されている。具体的には、例えば、電磁石81を右回り又は左回りに順に電流を交互にオンとオフに切り替えることによって、電磁石81によって形成される磁場を回転させる。好ましくは、反応槽90の中央に設けた攪拌機(図示省略)の回転方向(図中の液流方向)とは逆向きに磁場を回転させる。これにより磁場による固体粒子(澱物粒子)の移動方向と液流方向とは互いに逆向きになるので、液と澱物粒子との相対線速度が上がり、澱物フェライト化の反応効率が向上する。 5 and 6 show examples in which an electromagnet 81 is attached to a reaction vessel (reaction vessel) 90. FIG. As shown in the drawing, a plurality of electromagnets 81 are attached to the tank wall of the reaction vessel 90 at equal intervals, and each electromagnet is connected to a control unit (not shown). The current of each electromagnet 81 is controlled by the control unit. Specifically, for example, the magnetic field formed by the electromagnet 81 is rotated by switching the current alternately on and off in order clockwise or counterclockwise. Preferably, the magnetic field is rotated in the direction opposite to the rotation direction (liquid flow direction in the drawing) of a stirrer (not shown) provided in the center of the reaction tank 90. As a result, the moving direction of the solid particles (starch particles) by the magnetic field and the liquid flow direction are opposite to each other, so that the relative linear velocity between the liquid and the starch particles is increased, and the reaction efficiency of starch ferrite formation is improved. .

上記処理装置は、重金属含有水について優れた重金属除去効果を有する。本発明において重金属類含有水とは、重金属類を含む水を広く意味し、自然発生的および人為的に生じた各種の廃水や排水等を含み、例えば、工場排水や下水、海水、河川水、沼や湖池の水、地表の溜り水、河川等の堰止域の水、地下の流水や溜り水、暗渠の水などであって重金属類を含有するものを云う。なお、以下の説明において、これらの水を含めて排水等と云い、重金属類含有水について重金属類を含有する排水等と云う場合がある。 The said processing apparatus has the outstanding heavy metal removal effect about heavy metal containing water. In the present invention, heavy metal containing water broadly means water containing heavy metals, and includes various wastewater and wastewater generated naturally and artificially, for example, industrial wastewater and sewage, seawater, river water, This refers to water from marshes and lakes, surface pools, rivers and other dams, underground running water and pools, underdrains, etc. that contain heavy metals. In the following description, these waters may be referred to as waste water, and the heavy metal containing water may be referred to as waste water containing heavy metals.

また、本発明において重金属類とは、例えば、セレン、カドミウム、六価クロム、鉛、亜鉛、銅、ニッケル、ヒ素、アンチモンなどの重金属元素や金属元素などを云う。本発明の処理システムは排水等に含まれるこれらの汚染源となる重金属類の何れか1種および2種以上に対して優れた除去効果を有する。 In the present invention, heavy metals refer to heavy metal elements such as selenium, cadmium, hexavalent chromium, lead, zinc, copper, nickel, arsenic, and antimony, and metal elements. The treatment system of the present invention has an excellent removal effect with respect to any one or more of the heavy metals that are the sources of contamination contained in the waste water and the like.

重金属類含有水を添加槽10に導き、還元性鉄化合物を添加する。還元性鉄化合物としては、硫酸第一鉄(FeSO4)、または塩化第一鉄(FeCl2)などの第一鉄化合物を用いることができる。第一鉄化合物の添加量はFe2+イオン濃度400〜600mg/Lになる量が適当である。還元性鉄化合物を添加した排水を反応槽30に導入する。 The heavy metal-containing water is introduced into the addition tank 10 and the reducing iron compound is added. As the reducing iron compound, a ferrous compound such as ferrous sulfate (FeSO 4 ) or ferrous chloride (FeCl 2 ) can be used. The addition amount of the ferrous compound is appropriate such that the Fe 2+ ion concentration is 400 to 600 mg / L. Waste water to which the reducing iron compound is added is introduced into the reaction tank 30.

反応槽30には、還元性鉄化合物を添加した重金属類含有水と共に、固液分離工程から返送されたアルカリ性汚泥が混合される。このアルカリ性汚泥は後工程において固液分離された沈澱(汚泥)の一部または全部にアルカリを添加してpH11〜13に調整したものである。添加するアルカリ物質としては消石灰、生石灰、水酸化ナトリウムなどを用いることができる。アルカリ性汚泥を混合することによって、反応槽30のpHは8.5〜11、好ましくはpH9.0〜10に調整される。 The reaction tank 30 is mixed with the alkaline metal sludge returned from the solid-liquid separation step together with the heavy metal-containing water to which the reducing iron compound is added. This alkaline sludge is adjusted to pH 11 to 13 by adding alkali to a part or all of the precipitate (sludge) separated into solid and liquid in the subsequent step. As the alkaline substance to be added, slaked lime, quick lime, sodium hydroxide or the like can be used. By mixing the alkaline sludge, the pH of the reaction tank 30 is adjusted to 8.5 to 11, preferably pH 9.0 to 10.

反応槽30において、還元性鉄化合物を添加した重金属含有水とアルカリ性返送汚泥とを混合し、非酸化性雰囲気下で反応させることによって、還元性の鉄化合物沈澱を生成させる。この鉄化合物沈澱は、グリーンラストと鉄フェライトの混合物であり、還元性の沈澱である。 In the reaction tank 30, heavy metal-containing water to which a reducing iron compound is added and alkaline return sludge are mixed and reacted in a non-oxidizing atmosphere to generate a reducing iron compound precipitate. This iron compound precipitate is a mixture of green last and iron ferrite and is a reductive precipitate.

グリーンラストは第一鉄と第二鉄の水酸化物が層状をなす青緑色の物質であり、層間に重金属類のアニオンを取り込んだ構造を有し、例えば次式(1)によって表される。
〔FeII (6-x)FeIII x(OH)12x+〔Ax/n・yH2O〕x- …(1)
(0.9<x<4.2、Fe2+/全Fe=0.3〜0.85)。
Green last is a blue-green substance in which a hydroxide of ferrous iron and ferric iron forms a layer, and has a structure in which an anion of heavy metals is incorporated between layers, and is represented by, for example, the following formula (1).
[Fe II (6-x) Fe III x (OH) 12 ] x + [A x / n · yH 2 O] x- ... (1)
(0.9 <x <4.2, Fe 2+ / total Fe = 0.3 to 0.85).

また、鉄フェライトはFeIIの鉄(III)酸塩であり、マグネタイト(FeIIFeIII 24)を主体とするが、一部に重金属類の鉄酸塩を含むものでもよい。本発明の還元性の鉄化合物沈澱は、例えば、重金属類イオンがグリーンラストの層間に取り込まれ、重金属類を一部に含んだ状態で鉄フェライト化する。具体的には、例えば、6価セレン(SeO4 2-)は第一鉄化合物によって還元されて4価セレン(SeO3 2-)および元素セレンになり、これらはグリーンラストの層間に取り込まれた状態で沈澱化する。 Moreover, iron ferrites are Fe II iron (III) salt, but mainly of magnetite (Fe II Fe III 2 O 4 ), or those containing ferrate heavy metals in a part. In the reducing iron compound precipitate of the present invention, for example, heavy metal ions are taken in between the layers of the green last, and iron ferrite is formed in a state in which heavy metals are partially included. Specifically, for example, hexavalent selenium (SeO 4 2− ) is reduced by a ferrous compound to tetravalent selenium (SeO 3 2− ) and elemental selenium, which are taken in between the layers of green last. It precipitates in the state.

上記反応槽30は、上記還元性鉄化合物沈澱を生成させるために、空気の流入を遮断した密閉反応槽が用いられる。該反応槽30において、非酸化性雰囲気下、pH8.5〜11、好ましくはpH9.0〜10のアルカリ性下で反応させる。液温は10℃〜30℃程度で良く、加熱する必要はない。反応時間は30分〜3時間程度で良い。なお、反応槽が密閉されておらず、非酸化性雰囲気下ではないもの、またアルカリの程度が弱いものは、上記還元力を有する沈澱が生成せず、本処理装置と同様の効果を得ることはできない。 The reaction tank 30 is a sealed reaction tank in which the inflow of air is blocked in order to generate the reducible iron compound precipitate. In the reaction tank 30, the reaction is carried out in a non-oxidizing atmosphere under alkaline conditions of pH 8.5-11, preferably pH 9.0-10. The liquid temperature may be about 10 ° C. to 30 ° C. and does not need to be heated. The reaction time may be about 30 minutes to 3 hours. In addition, if the reaction vessel is not sealed and is not in a non-oxidizing atmosphere, or if the alkali is weak, precipitates having the above reducing power will not be generated, and the same effect as this treatment apparatus can be obtained. I can't.

密閉反応槽からスラリーを抜き出してアルカリ添加を経て再び密閉反応槽に返送する循環経路の何れかの工程において、上記スラリーないし汚泥と空気との接触を調整して鉄化合物の酸化を抑制するのが好ましい。具体的には、例えば、上部が開放された固液分離槽、または上部開口を有するアルカリ添加槽を用い、固液分離の際に沈殿物スラリーと空気を接触させ、または分離した汚泥にアルカリを添加する際に汚泥と空気とを接触させると共に、その接触時間や接触面積等を調整すれば良い。 In any step of the circulation path in which the slurry is extracted from the sealed reaction tank and returned to the sealed reaction tank again after alkali addition, the contact of the slurry or sludge with air is adjusted to suppress oxidation of the iron compound. preferable. Specifically, for example, a solid-liquid separation tank having an open top or an alkali addition tank having an upper opening is used, and in the solid-liquid separation, the precipitate slurry and air are brought into contact with each other, or alkali is added to the separated sludge. What is necessary is just to adjust the contact time, the contact area, etc. while making sludge and air contact when adding.

本発明の処理装置においては、グリーンラストと鉄フェライトの混合物からなる上記鉄化合物沈澱が還元力を有するように、該沈澱の2価鉄イオンと全鉄イオンの比〔Fe2+/Fe(T)〕が0.4〜0.8であるように沈澱を生成させることが好ましく、上記鉄イオン比を0.55〜0.65に制御するのが更に好ましい。この比が上記範囲を外れると重金属類の還元が不十分になり、あるいは澱物の沈降性が劣化するので好ましくない。上記還元性の鉄化合物沈澱を生成させることによって、排水等に含まれる重金属類が還元され、容易に沈澱に取り込まれる。 In the treatment apparatus of the present invention, the ratio of the divalent iron ions to the total iron ions [Fe 2+ / Fe (T )] Is preferably 0.4 to 0.8, and the iron ion ratio is more preferably controlled to 0.55 to 0.65. When this ratio is out of the above range, the reduction of heavy metals becomes insufficient, or the sedimentation property of starch deteriorates, which is not preferable. By producing the reducible iron compound precipitate, heavy metals contained in the waste water and the like are reduced and easily taken into the precipitate.

反応槽30にアルカリ性汚泥の返送を繰り返し、還元性鉄化合物を添加した排水等との反応を繰り返すことによって、最初は深青緑色であった沈澱がしだいにグリーンラストが酸化して鉄フェライト化することによって黒色に変化する。グリーンラストの大部分が鉄フェライトになると還元性がなくなるので、上記鉄化合物沈澱の2価鉄イオンと全鉄イオンの比〔Fe2+/Fe(T)〕を上記範囲内に制御することによって還元性のある沈澱を生成させる。 By repeating the return of alkaline sludge to the reaction tank 30 and repeating the reaction with wastewater to which a reducing iron compound is added, the green rust is gradually oxidized to iron ferrite by the precipitation that was initially deep blue-green. Changes to black. Since the reducibility is lost when most of the green rust becomes iron ferrite, the reducibility can be reduced by controlling the ratio of divalent iron ions to total iron ions [Fe2 + / Fe (T)] within the above range. To produce a precipitate.

本発明の処理装置では、上記還元性汚泥(鉄化合物沈澱)を分離してその一部または全部をアルカリ化して反応槽に返送し、非酸化性雰囲気下で反応させ、再び還元性汚泥を沈澱させることを繰り返すことによって、汚泥(沈澱)の還元性を維持しつつ鉄フェライト化するので沈澱の圧密化が進み、澱物の濃度が格段に高まるので重金属類の除去効果が向上する。因みに、水酸化鉄を主体とした沈澱(汚泥)は嵩高く、脱水処理の負担が大きい。また、本発明の処理装置では、沈澱を形成している鉄フェライトはマグネタイトを主体とするので磁性を帯びており、反応槽に変動磁場を与えることによって、フェライト化が促進され、また固液分離槽に変動磁場を与えることによって、沈殿の凝集を促し、分離効果を高めることができる。 In the treatment apparatus of the present invention, the reducing sludge (iron compound precipitation) is separated, and part or all of the reduced sludge is alkalinized and returned to the reaction vessel, reacted in a non-oxidizing atmosphere, and the reducing sludge is precipitated again. By repeating this process, iron ferrite is formed while maintaining the reducibility of the sludge (precipitation), so that the consolidation of the precipitation proceeds and the concentration of the starch is remarkably increased, thereby improving the effect of removing heavy metals. Incidentally, precipitation (sludge) mainly composed of iron hydroxide is bulky and has a heavy dehydration burden. Further, in the processing apparatus of the present invention, the iron ferrite forming the precipitate is magnetized because it is mainly composed of magnetite. By applying a variable magnetic field to the reaction vessel, ferritization is promoted, and solid-liquid separation is performed. By applying a fluctuating magnetic field to the tank, aggregation of the precipitate can be promoted and the separation effect can be enhanced.

反応槽30から排出されたスラリーは、例えばシックナーなどの固液分離手段に導き、汚泥を槽底に沈降させて分離する。この澱物を固液分離して重金属類を除去することができる。また、既に述べたように、汚泥の一部または全部にアルカリを添加してpH11〜13に調整して反応槽30に戻し、反応槽30において沈澱生成反応を繰り返す。返送する汚泥の割合(返送汚泥の循環比)は反応槽30で生成する沈澱の2価鉄イオンと全鉄イオンの比〔Fe2+/Fe(T)〕が上記範囲内になるように定めればよい。なお、本発明の処理方法は、バッチ式または連続式の何れの形式でも実施することができる。 The slurry discharged from the reaction tank 30 is guided to a solid-liquid separation means such as a thickener, for example, and sludge is settled on the tank bottom to be separated. The starch can be solid-liquid separated to remove heavy metals. Moreover, as already stated, an alkali is added to part or all of sludge, it adjusts to pH 11-13, and it returns to the reaction tank 30, The precipitation production | generation reaction is repeated in the reaction tank 30. If the ratio of sludge to be returned (circulation ratio of returned sludge) is determined so that the ratio [Fe2 + / Fe (T)] of the divalent iron ions and total iron ions in the precipitate generated in the reaction tank 30 is within the above range. Good. The treatment method of the present invention can be carried out in either a batch type or a continuous type.

図2に示す処理装置には、還元性鉄化合物添加槽10の前に、重金属類含有水に鉄化合物またはアルミニウム化合物を添加して沈澱を生成させる槽60と、該沈殿を除去する固液分離槽70が設けた前処理工程が形成されている。該前処理工程において、重金属類含有水に鉄化合物を添加してアルカリを加え、アルカリ性下で鉄水酸化物を生成させることによって、ケイ酸イオン、アルミニウムイオン、微量有機物の少なくとも何れかを鉄水酸化物沈澱と共に沈澱化し、この沈澱を固液分離して除去する。鉄化合物としては塩化第二鉄などの第二鉄化合物が好ましい。鉄化合物に代えてアルミニウム化合物を用いてもよい。アルミニウム化合物を添加してアルカリを加え、アルカリ性下でアルミニウム水酸化物を沈殿させる。この沈殿にケイ酸イオンや微量有機物が取り込まれて沈殿化するので、これを固液分離して排水から除去することができる。 The processing apparatus shown in FIG. 2 includes a tank 60 for adding an iron compound or an aluminum compound to heavy metal-containing water to form a precipitate before the reducing iron compound adding tank 10 and a solid-liquid separation for removing the precipitate. A pretreatment process provided by the tank 70 is formed. In the pretreatment step, an iron compound is added to heavy metal-containing water, an alkali is added, and an iron hydroxide is generated under alkalinity, whereby at least one of silicate ions, aluminum ions, and trace organic substances is added to the iron water. It precipitates with the oxide precipitate, which is removed by solid-liquid separation. A ferric compound such as ferric chloride is preferred as the iron compound. An aluminum compound may be used in place of the iron compound. An aluminum compound is added, an alkali is added, and an aluminum hydroxide is precipitated under alkalinity. Since silicate ions and trace organic substances are taken into the precipitate and precipitated, it can be solid-liquid separated and removed from the waste water.

排水中のケイ酸イオン、アルミニウムイオン、微量有機物は反応槽でのフェライト化を阻害する原因となるので、前処理工程において予めこれらを除去することによって、フェライト化を円滑に進め、重金属類除去の処理効果を高めることができる。 Silicate ions, aluminum ions, and trace amounts of organic substances in the wastewater cause the ferritization in the reaction tank, so by removing them in advance in the pretreatment process, the ferritization is facilitated and heavy metals are removed. The processing effect can be enhanced.

また、上記反応槽30は複数の槽を直列に設け、生成したスラリーを段階的に移し替えてフェライト化反応を進めると良い。変動磁場手段50は任意の反応槽に設ければよい。さらに、反応槽上部は蓋材で覆われた形状にし、該蓋材には攪拌機の軸部材が挿通する小孔を設けると共に該小孔に向かって上向きの傾斜を有する形状にすると良い。 Moreover, the said reaction tank 30 is good to provide a some tank in series, and to advance the ferrite formation reaction by transferring the produced | generated slurry in steps. The variable magnetic field means 50 may be provided in any reaction tank. Further, the upper part of the reaction tank is preferably covered with a cover material, and the cover material is provided with a small hole through which the shaft member of the stirrer is inserted and has a shape having an upward slope toward the small hole.

反応槽を上記形状にすることによって、反応槽内部は上記小孔を通じて外気との連通が制限されて非酸化性雰囲気に保たれ、また槽内で発生したガスは蓋材の傾斜に沿って小孔に導かれ、上記軸部材の周りの僅かな隙間を通じて外部に抜け出すことができる。 By making the reaction vessel in the above shape, the inside of the reaction vessel is kept in a non-oxidizing atmosphere with limited communication with outside air through the small holes, and the gas generated in the reaction vessel is reduced along the inclination of the lid. It is guided to the hole and can be pulled out through a slight gap around the shaft member.

図1および図2の装置例は、密閉反応槽を用いて還元性鉄化合物沈澱を生成させる処理工程に関するが、本発明は上部が開口した開放型の反応槽を用いる場合にも適用することができる。 1 and FIG. 2 relates to a treatment process for producing a reduced iron compound precipitate using a closed reaction vessel, but the present invention can also be applied to the case of using an open reaction vessel with an open top. it can.

本発明の処理装置を示す模式図Schematic diagram showing the processing apparatus of the present invention 本発明の前処理工程を含む処理装置を示す模式図The schematic diagram which shows the processing apparatus containing the pre-processing process of this invention 本発明の処理システムにおいて、シックナーに電磁石を装着した構成例の概念図In the processing system of this invention, the conceptual diagram of the structural example which attached the electromagnet to the thickener 本発明の処理システムにおいて、シックナーに電磁石を装着した構成例の概念図In the processing system of this invention, the conceptual diagram of the structural example which attached the electromagnet to the thickener 本発明の処理システムにおいて、反応槽に電磁石を装着した構成例の概念図In the processing system of this invention, the conceptual diagram of the example of a structure which attached the electromagnet to the reaction tank 図5の構成例の概念斜視図Conceptual perspective view of the configuration example of FIG.

符号の説明Explanation of symbols

10−還元性鉄化合物添加槽、20−アルカリ添加槽、30−反応槽、40−固液分離槽、50−変動磁場手段、60−沈殿化槽、70−固液分離槽、80−制御部、81−電磁石、82−シックナー、90−反応容器(反応槽)。 10-reducing iron compound addition tank, 20-alkali addition tank, 30-reaction tank, 40-solid-liquid separation tank, 50-variable magnetic field means, 60-precipitation tank, 70-solid-liquid separation tank, 80-control unit , 81—electromagnet, 82—thickener, 90—reaction vessel (reaction vessel).

Claims (8)

重金属類含有水と還元性鉄化合物とを混合して沈殿を生じさせる反応槽、該反応槽から抜き出したスラリーを固液分離する槽を有する処理装置において、上記反応槽または固液分離槽の少なくとも何れかに変動磁場を与える手段を有しており、反応槽において磁場を変動させながら沈澱生成を促し、または固液分離槽において磁場を変動させなら固液分離を促すことを特徴とする重金属類含有水の処理装置。
In a processing tank having a reaction tank that mixes heavy metal-containing water and a reducible iron compound to cause precipitation, and a tank that solid-liquid separates the slurry extracted from the reaction tank, at least one of the reaction tank or the solid-liquid separation tank Heavy metals having means for applying a variable magnetic field to any of them, promoting precipitation generation while changing the magnetic field in the reaction tank, or promoting solid-liquid separation if the magnetic field is changed in the solid-liquid separation tank Water treatment equipment.
請求項1の処理装置において、重金属類含有水と還元性鉄化合物とを混合して沈澱を生じさせる密閉型反応槽を有し、該反応槽から抜き出したスラリーを固液分離する槽、分離した沈殿物(汚泥)の一部または全部にアルカリを添加する槽、アルカリ化した汚泥を上記密閉反応槽に返送する管路を有し、該密閉反応槽において、非酸化性雰囲気下、アルカリ性下で還元性の鉄化合物沈澱を生成する一方、密閉反応槽からスラリーを抜き出してアルカリ添加を経て再び密閉反応槽に返送する循環経路の何れかの工程において上記スラリーないし汚泥と空気との接触を調整して鉄化合物の酸化を抑制し、上記各工程を繰り返して重金属類含有水を処理する装置において、上記反応槽または固液分離槽の少なくとも何れかに変動磁場を与える手段を有する重金属類含有水の処理装置。
The treatment apparatus according to claim 1, further comprising: a sealed reaction tank for mixing the heavy metal-containing water and the reducing iron compound to cause precipitation, and a tank for solid-liquid separation of the slurry extracted from the reaction tank. A tank for adding alkali to part or all of the precipitate (sludge), a pipe for returning the alkaliized sludge to the closed reaction tank, and in the closed reaction tank under a non-oxidizing atmosphere and under alkaline conditions While the reductive iron compound precipitate is generated, the contact between the slurry or sludge and air is adjusted in any step of the circulation path in which the slurry is extracted from the sealed reaction tank and returned to the sealed reaction tank through alkali addition. In the apparatus for suppressing oxidation of the iron compound and treating the heavy metal-containing water by repeating the above steps, means for applying a varying magnetic field to at least one of the reaction tank and the solid-liquid separation tank Heavy metals containing water processing apparatus.
反応槽の周囲または固液分離槽の隔壁に磁石を配設し、該磁石を回転または振動させることによって、該磁石によって形成される磁場を変動させる請求項1または2に記載する排水の処理装置。
The wastewater treatment apparatus according to claim 1 or 2, wherein a magnet is disposed around the reaction tank or in a partition wall of the solid-liquid separation tank, and the magnetic field formed by the magnet is changed by rotating or vibrating the magnet. .
反応槽の周囲または固液分離槽の隔壁に電磁石を配設し、該電磁石の電流を制御することによって、該電磁石によって形成される磁場を変動させる請求項1または2に記載する排水の処理装置。
The wastewater treatment apparatus according to claim 1 or 2, wherein an electromagnet is disposed around the reaction tank or in a partition wall of the solid-liquid separation tank, and the electric field of the electromagnet is controlled to vary the magnetic field formed by the electromagnet. .
請求項1〜4の何れかの処理装置において、重金属類含有水と還元性鉄化合物とを混合反応させる反応槽の前に、重金属類含有水に還元性鉄化合物を添加する槽を有する重金属類含有水の処理装置。
In the processing apparatus in any one of Claims 1-4, the heavy metals which have a tank which adds a reducing iron compound to heavy metal containing water before the reaction tank which carries out the mixing reaction of heavy metal containing water and a reducing iron compound Water treatment equipment.
請求項1〜5の何れかの処理装置において、重金属類含有水に還元性鉄化合物を添加する槽の前に、重金属類含有水に鉄化合物またはアルミニウム化合物を添加する槽、および生成した沈澱を固液分離する槽が設けられている重金属類含有水の処理装置。
In the processing apparatus of any one of Claims 1-5, the tank which adds an iron compound or an aluminum compound to heavy metal containing water before the tank which adds a reducing iron compound to heavy metal containing water, and produced | generated precipitation An apparatus for treating heavy metal-containing water provided with a tank for solid-liquid separation.
請求項1〜6の何れかの処理装置において、複数の反応槽が直列に設けられており、任意の反応槽およびまたは固液分離槽に変動磁場を与える手段が設けられている重金属類含有水の処理装置。
The processing apparatus according to any one of claims 1 to 6, wherein a plurality of reaction tanks are provided in series, and a means for applying a variable magnetic field to any reaction tank and / or solid-liquid separation tank is provided. Processing equipment.
請求項1〜7の何れかの処理装置において、反応槽の上部が蓋材で覆われており、該蓋材は攪拌機の軸部材が挿通する小孔を有し、かつ該蓋は上記小孔に向かって上向きの傾斜を有しており、反応槽内部は上記小孔を通じて外気との連通が制限されて非酸化性雰囲気に保たれている重金属類含有水の処理装置。

The processing apparatus according to any one of claims 1 to 7, wherein an upper portion of the reaction tank is covered with a lid member, the lid member has a small hole through which a shaft member of a stirrer is inserted, and the lid is the small hole. The apparatus for treating heavy metal-containing water, which has an upward slope toward the inside and the inside of the reaction tank is kept in a non-oxidizing atmosphere with limited communication with outside air through the small holes.

JP2005373333A 2004-12-27 2005-12-26 Apparatus for treating heavy metals-containing water Pending JP2007117984A (en)

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Publication number Priority date Publication date Assignee Title
CN102001762A (en) * 2009-08-31 2011-04-06 三菱综合材料株式会社 Process method of a selenium-containing discharge water
CN109293126A (en) * 2018-11-01 2019-02-01 艾特克控股集团股份有限公司 One kind is based on modified ferritic sewage-treatment plant
CN110282708A (en) * 2019-07-26 2019-09-27 农业部沼气科学研究所 The device and method of heavy metal complex is removed in a kind of biogas slurry

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JP2002102863A (en) * 2000-09-29 2002-04-09 Japan Science & Technology Corp Treating method for geothermal water

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Publication number Priority date Publication date Assignee Title
CN102001762A (en) * 2009-08-31 2011-04-06 三菱综合材料株式会社 Process method of a selenium-containing discharge water
CN109293126A (en) * 2018-11-01 2019-02-01 艾特克控股集团股份有限公司 One kind is based on modified ferritic sewage-treatment plant
CN110282708A (en) * 2019-07-26 2019-09-27 农业部沼气科学研究所 The device and method of heavy metal complex is removed in a kind of biogas slurry
CN110282708B (en) * 2019-07-26 2022-04-05 农业部沼气科学研究所 Device and method for removing heavy metal complex from biogas slurry

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