JP2021037483A - Method for manufacturing water purification material - Google Patents

Method for manufacturing water purification material Download PDF

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JP2021037483A
JP2021037483A JP2019161395A JP2019161395A JP2021037483A JP 2021037483 A JP2021037483 A JP 2021037483A JP 2019161395 A JP2019161395 A JP 2019161395A JP 2019161395 A JP2019161395 A JP 2019161395A JP 2021037483 A JP2021037483 A JP 2021037483A
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clay
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JP6653040B1 (en
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眞也 竹内
Shinya Takeuchi
眞也 竹内
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Cap Seeds Co Ltd
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Abstract

To provide a method for producing a water purification material that purifies oily water such as produced water.SOLUTION: Reduction firing comprises the following first to sixth steps. First step: Wood section clay and plant-derived organic matter are kneaded and molded by adding water. Second step: The kneaded molded product is set in a furnace and heated at 300°C or lower to remove water in the molded product. Third step: The molded product from which water has been removed is held at 400 to 500°C and completely carbonized. Fourth step: A firing temperature is raised to 750 to 850°C, and by maintaining this temperature, bases and nitrates in the wood section clay are gasified to form continuous pores. Fifth step: The temperature is raised to 1050°C, an environment inside the furnace is set in a reduced state, and the continuous pore surface is vitrified. Sixth step: In the reduced state, the temperature is raised to 1250 to 1300°C, and by maintaining this temperature, quartz, alumina and metal are welded to the vitrified portion to activate the pore surface.SELECTED DRAWING: Figure 1

Description

本発明は、プロデュースウォータ(produced water)などの油分を含んだ水を浄化する浄化材の製造方法に関する。 The present invention relates to a method for producing a purifying material for purifying oil-containing water such as produced water.

水を油井に注入する水攻法によって油の産出量を回復することが行われている。プロデュースウォータは水攻法で使用された水であり、石油工業において使用する専門語である。このプロデュースウォータには油分およびガスだけでなく、重金属および天然に存在する微量の放射性物質が含まれているため、そのまま河川や海に捨てることはできない。 Oil production is being restored by a water attack method in which water is injected into an oil well. Produce water is the water used in the water attack method and is a technical term used in the oil industry. This produced water contains not only oil and gas, but also heavy metals and trace amounts of naturally occurring radioactive substances, so it cannot be discarded as it is in rivers and the sea.

水浄化材としてポーラスセラミックを用いた先行技術として、特許文献1〜3が挙げられる。
特許文献1には、粘土・珪石並びに水酸化アルミニウムから選んだ二種以上のもの、例えば粘土と珪石を基材として、これに水酸化アルミニウムを混合物又は粘土と珪石の混合物に気泡形成用材料として、例えばオガクズやモミガラを添加して混合し、この混合物をブロック状態で又は他の適当な形状で乾燥させ、次いで焼成することにより気泡形成用材料が焼失してポーラスとなるセラミックが開示されている。(第4段落)
Prior arts using porous ceramic as a water purifying material include Patent Documents 1 to 3.
In Patent Document 1, two or more kinds selected from clay / silicate and aluminum hydroxide, for example, clay and silicate are used as a base material, and aluminum hydroxide is used as a base material in a mixture or a mixture of clay and silicate as a material for forming bubbles. Disclosed are ceramics in which, for example, ogakuzu and fir-gara are added and mixed, and the mixture is dried in a block state or in another suitable shape, and then fired to burn out the bubble-forming material to become porous. .. (4th paragraph)

特許文献2には、ポーラスセラミックを用いた有機塩素化合物を含有する廃液・排水の処理方法が開示されている。上記のポーラスセラミックの製法としては、瀬戸地方から採取した粘土とオガクズなどの気孔形成材料と水を混合し、適宜形状に成形後、乾燥させ、該乾燥成型体の品温を成型体中の気孔形成材料の自燃により5〜15時間かけて、常温から600〜800℃まで昇温させ、600〜800℃で3〜7時間保持した後、1200〜1500℃まで昇温させ、1200〜1500℃で4〜8時間焼成した後、クラッシャー処理することが開示されている。 Patent Document 2 discloses a method for treating waste liquid / waste water containing an organic chlorine compound using porous ceramics. As the above-mentioned method for producing porous ceramics, clay collected from the Seto region, a pore-forming material such as sawdust, and water are mixed, molded into an appropriate shape, dried, and the temperature of the dried molded body is adjusted to the pores in the molded body. By self-combustion of the forming material, the temperature is raised from room temperature to 600 to 800 ° C. over 5 to 15 hours, held at 600 to 800 ° C. for 3 to 7 hours, then raised to 1200 to 1500 ° C., and at 1200 to 1500 ° C. It is disclosed that the crusher treatment is performed after firing for 4 to 8 hours.

特許文献3には、静電気を吸収、帯電、放電する微細孔を有する粉体状のセラミックが提案されている。この粉体状のセラミックは塗料と混ぜて使うことで、船底等にフジツボ、カラス貝等の貝類や海藻等の海棲生物が付着するのを防止するためのものである。 Patent Document 3 proposes a powdery ceramic having micropores that absorb, charge, and discharge static electricity. This powdery ceramic is used by mixing it with paint to prevent shellfish such as barnacles and crows and marine organisms such as seaweed from adhering to the bottom of the ship.

また、粘土鉱物の一種として木節が知られている。この木節は、花崗岩の風化物であるカオリナイト(AlSl(OH))が沼地の植物や流木とともに埋没沈積したものであり、有機物を特に豊富に含んでいる。この木節に関する先行技術として特許文献4〜6が挙げられる。 In addition, wood knots are known as a type of clay mineral. This knot is a granite weathered kaolinite (Al 2 Sl 2 O 5 (OH) 4 ) buried and deposited together with swamp plants and driftwood, and is particularly rich in organic matter. Patent Documents 4 to 6 can be mentioned as prior arts relating to this wood section.

特許文献4では、木節を生物の成育を促進したり、水や食品などを、安全で害のないものに変える機能性セラミックスとして用いている。 In Patent Document 4, wood nodes are used as functional ceramics that promote the growth of living organisms and change water, food, etc. into safe and harmless ones.

特許文献5では、磁気カードや磁気フィルム等の炭化物が顕著な水質浄化能力を発現する点に着目し、これを粘結剤で固めて所望の形状とすることが提案されている。この粘結剤の一例として、ベントナイト、マグネサイト、軽焼マグネシウム、水酸化マグネシウムや黒糖溶液と共に木節粘土が挙げられている。
つまり木節粘土は粘結剤として挙げられ、有害物質の分解に用いられていない。
Patent Document 5 pays attention to the fact that carbides such as magnetic cards and magnetic films exhibit remarkable water purification ability, and proposes to solidify them with a binder to obtain a desired shape. As an example of this binder, bentonite, magnesite, light-baked magnesium, magnesium hydroxide and brown sugar solution as well as wood-knot clay are mentioned.
In other words, Kibushi clay is listed as a binder and is not used to decompose harmful substances.

特許文献6では、飲食店などのグリーストラップに溜まった油濁物(固形油分+液体油)を含む油濁物含有有機排水を浄化する浄化材として、イオン交換を行う活性土壌とマイナスイオンを発生する成分(たとえばセラミック)を含んだものが提案され、木節粘土は上記の主成分ではなくその他の添加物の1つとして挙げられている。(段落0012) In Patent Document 6, active soil for ion exchange and negative ions are generated as a purifying material for purifying organic wastewater containing oil turbidity (solid oil + liquid oil) accumulated in a grease trap of a restaurant or the like. It has been proposed that the clay contains a component (for example, ceramic), and the wood-knot clay is listed as one of the other additives instead of the above-mentioned main component. (Paragraph 0012)

油分(有機物)を含む海水の浄化システムとして、非特許文献1及び2が挙げられる。
非特許文献1には、上流側から順に、UF(ウルトラファイン膜)、CAF(セラミック製吸着フィルタ)及びRO(逆浸透膜)を配置した海水浄化システムが開示されている。
Non-Patent Documents 1 and 2 are mentioned as seawater purification systems containing oil (organic matter).
Non-Patent Document 1 discloses a seawater purification system in which UF (ultrafine membrane), CAF (ceramic adsorption filter) and RO (reverse osmosis membrane) are arranged in order from the upstream side.

また非特許文献2には、セラミック製平膜の外側の油分(有機物)を含む海水に圧力をかけることで、油分よりも小さな水分子が平膜を透過し、ろ過水として回収される構造が開示されている。 Further, Non-Patent Document 2 has a structure in which water molecules smaller than oil permeate the flat membrane and are recovered as filtered water by applying pressure to seawater containing oil (organic matter) on the outside of the ceramic flat membrane. It is disclosed.

特開昭59−087091号公報JP-A-59-087091 特開平10−118643号公報Japanese Unexamined Patent Publication No. 10-18643 特開2012−131961号公報Japanese Unexamined Patent Publication No. 2012-131961 特開平11−079864号公報Japanese Unexamined Patent Publication No. 11-079864 特開2000−246277号公報Japanese Unexamined Patent Publication No. 2000-246277 特開2006−026516号公報Japanese Unexamined Patent Publication No. 2006-026516

海水淡水化前処理用セラミックス吸着フィルタの開発 日立金属株式会社 2019年ニュースリリースDevelopment of Ceramic Adsorption Filter for Seawater Desalination Pretreatment Hitachi Metals, Ltd. 2019 News Release セラミック平膜システム 明電舎 製品・サービスCeramic flat film system Meidensha products and services

多孔質セラミックは水の浄化材として用いられているが、プロデュースウォータなどの油分を大量に含む水の浄化材として使用する場合、孔径が油分子よりも小さいと油分を除去することができず、油分子の除去に適した孔径としても目詰まりを起こし、連続的な浄化には使用することができない。 Porous ceramics are used as a water purifier, but when used as a water purifier containing a large amount of oil such as produce water, if the pore size is smaller than the oil molecules, the oil cannot be removed. Even if the pore size is suitable for removing oil molecules, it causes clogging and cannot be used for continuous purification.

ゼオライトなどの粘度鉱物を焼成しても、目が細かすぎ、またオガクズなどの気孔形成材料と混合した後に焼成してオガクズなどをガス化して除去し、水が入り込める大きさの連続孔を形成しても、油分子によって目詰まりを起こしてしまう。 Even if a viscous mineral such as zeolite is fired, the mesh is too fine, and after mixing with a pore-forming material such as sawdust, it is fired to gasify and remove sawdust, forming continuous pores large enough to allow water to enter. However, oil molecules cause clogging.

非特許文献1に開示されるシステムでは、UFとCAFを頻繁に再生しなければならず、非特許文献2では放水によって平膜表面を頻繁に洗浄する必要があり、メンテナンスが面倒である。 In the system disclosed in Non-Patent Document 1, UF and CAF must be regenerated frequently, and in Non-Patent Document 2, the flat membrane surface needs to be frequently washed by water discharge, which is troublesome to maintain.

木節粘土は有機物(炭化物)などの不純物を多量に含む二次粘度であり、焼成により上記炭化物をガラス化すると、このガラス化した表面には石英、アルミナ及び金属が融着して賦活化され、この賦活化した表面の触媒作用により油分を分解する点に着目して本願発明をなした。 Kibushi clay has a secondary viscosity containing a large amount of impurities such as organic substances (carbides), and when the carbides are vitrified by firing, quartz, alumina, and metals are fused and activated on the vitrified surface. The present invention has been made by paying attention to the fact that oil is decomposed by the catalytic action of this activated surface.

第一発明は還元焼成により浄化材を製造する方法であり、具体的には以下の工程1〜6から構成される。
第1工程:木節粘土と植物由来の有機物とを水を加えて混錬して成形する。
第2工程:前記混錬した成形体を炉内にセットし、300℃以下で加熱し成形体中の水分を除去する。
第3工程:水分が除去された成形体を400〜500℃に保持し完全に炭化せしめる。
第4工程:焼成温度を750〜850℃まで上昇させ、この温度で温度を維持することで木節粘土中の塩基、硝酸塩をガス化せしめ、連続した細孔を形成する。
第5工程:1050℃まで昇温させると共に炉内環境を還元状態とし、前記連続した細孔表面をガラス化する。
第6工程:還元状態で1250〜1300℃まで昇温し、この温度を維持することで、ガラス化した部分に石英、アルミナ及び金属を溶着させ、細孔表面を賦活化する。
The first invention is a method for producing a purifying material by reduction firing, and specifically comprises the following steps 1 to 6.
First step: Kibushi clay and plant-derived organic matter are kneaded and molded by adding water.
Second step: The kneaded molded product is set in a furnace and heated at 300 ° C. or lower to remove water in the molded product.
Third step: The molded product from which water has been removed is held at 400 to 500 ° C. and completely carbonized.
Fourth step: The firing temperature is raised to 750 to 850 ° C., and the temperature is maintained at this temperature to gasify the bases and nitrates in the knot clay to form continuous pores.
Fifth step: The temperature is raised to 1050 ° C., the environment inside the furnace is reduced, and the continuous pore surface is vitrified.
Sixth step: The temperature is raised to 1.25 to 1300 ° C. in the reduced state, and by maintaining this temperature, quartz, alumina and metal are welded to the vitrified portion to activate the pore surface.

第2発明は酸化焼成より浄化材を製造する方法であり、具体的には以下の工程1〜6から構成される。
第1工程:木節粘土と植物由来の有機物とを水を加えて混錬して成形する。
第2工程:前記混錬した成形体を炉内にセットし、300℃以下で加熱し成形体中の水分を除去する。
第3工程:水分が除去された成形体を400〜500℃に保持し完全に炭化せしめる。
第4工程:焼成温度を750〜850℃まで上昇させ、この温度で温度を維持することで木節粘土中の塩基、硝酸塩をガス化せしめ、連続した細孔を形成する。
第5工程:950℃まで炉内の酸化状態を維持したまま昇温することで前記連続した細孔表面をガラス化する。
第6工程:酸化状態で1200〜1300℃まで昇温し、この温度を維持することで、ガラス化した部分に石英、アルミナ及び金属を溶着させ、細孔表面を賦活化する。
The second invention is a method for producing a purifying material by oxidative firing, and specifically comprises the following steps 1 to 6.
First step: Kibushi clay and plant-derived organic matter are kneaded and molded by adding water.
Second step: The kneaded molded product is set in a furnace and heated at 300 ° C. or lower to remove water in the molded product.
Third step: The molded product from which water has been removed is held at 400 to 500 ° C. and completely carbonized.
Fourth step: The firing temperature is raised to 750 to 850 ° C., and the temperature is maintained at this temperature to gasify the bases and nitrates in the knot clay to form continuous pores.
Fifth step: The continuous pore surface is vitrified by raising the temperature to 950 ° C. while maintaining the oxidized state in the furnace.
Sixth step: The temperature is raised to 1200 to 1300 ° C. in the oxidized state, and by maintaining this temperature, quartz, alumina and metal are welded to the vitrified portion to activate the pore surface.

本発明に係る浄化材(CAPS:Continuous & Amorphous Porous Surfaces)の製造方法によれば、浄化材は連続した細孔の表面がガラス化し、このガラス化した表面に石英、アルミナ及び金属が融着して賦活化しているため、水中に含まれる油分が接触すると分解され除去される。
CAPSには油分子が入り込める程度の連続孔が形成されており、その孔の表面には木節に含まれている金属(重金属)の一部が露出ている。この金属が触媒の役割を果たして油分を分解する。
According to the method for producing a purifying material (CAPS: Continuous & Amorphous Porous Surfaces) according to the present invention, the surface of continuous pores of the purifying material is vitrified, and quartz, alumina and metal are fused to the vitrified surface. When the oil contained in the water comes into contact with the oil, it is decomposed and removed.
The CAPS has continuous pores that allow oil molecules to enter, and a part of the metal (heavy metal) contained in the wood nodes is exposed on the surface of the pores. This metal acts as a catalyst and decomposes oil.

本発明方法によって製造される浄化材は細孔の表面に油分を吸着するのではないため、目詰まりをおこすことなく、長期間メンテナンスフリーで使用することができる。 Since the purifying material produced by the method of the present invention does not adsorb oil on the surface of the pores, it can be used maintenance-free for a long period of time without causing clogging.

還元焼成にて浄化材を製造する際の温度管理の一例を示すグラフGraph showing an example of temperature control when manufacturing a purifying material by reduction firing 酸化焼成にて浄化材を製造する際の温度管理の一例を示すグラフGraph showing an example of temperature control when manufacturing a purifying material by oxidative firing 本発明方法で製造した浄化材の写真Photograph of the purifying material manufactured by the method of the present invention 本発明方法で製造した浄化材の拡大写真Enlarged photograph of the purifying material produced by the method of the present invention 木節粘土のみを材料とした比較例の拡大写真Enlarged photograph of a comparative example using only Kibushi clay as a material

先ず、木節粘土と植物由来の有機物を水に混錬して成形し、出発材料とする。木節粘土、植物由来の有機物及び水の混合割合(重量%)としては、80〜50:20〜50が好ましい。木節粘土はゼオライトと比較し、有機物および金属を多量に含み、焼成後の表面が賦活化されやすい。
植物由来の有機物としてはオガクズ、木端などが挙げられる。また、好ましい大きさとしては、焼成後に形成される連続孔の径が油分子侵入できる大きさとする。
また、上記の材料以外にネフェリン(霞石)を加えるようにしてもよい。
First, Kibushi clay and plant-derived organic matter are kneaded with water and molded to be used as a starting material. The mixing ratio (% by weight) of the wood-knot clay, the organic matter derived from the plant, and water is preferably 80 to 50:20 to 50. Compared to zeolite, wood-knot clay contains a large amount of organic substances and metals, and the surface after firing is easily activated.
Examples of plant-derived organic matter include sawdust and wood edges. Further, as a preferable size, the diameter of the continuous pores formed after firing is set to a size that allows oil molecules to penetrate.
In addition to the above materials, nepheline (nepheline) may be added.

上記の材料を混錬し、加圧成形や流し込み(泥漿成形)にて所定形状に成形する。次いで、図1に示すように、300℃以下の温度で成形体中の水分を除去する。 The above materials are kneaded and molded into a predetermined shape by pressure molding or pouring (slurry molding). Then, as shown in FIG. 1, the water content in the molded product is removed at a temperature of 300 ° C. or lower.

この後、昇温して行くと、400〜500℃の間で焼成が開始し、自燃が終了して完全炭化する。そして、このまま昇温を継続すると570℃付近において賦活化と成形の膨張が始まる。 After that, when the temperature is raised, firing starts between 400 and 500 ° C., self-combustion ends, and complete carbonization occurs. Then, if the temperature rise is continued as it is, activation and expansion of molding start at around 570 ° C.

この後、600℃付近から50℃/hの昇温速度で約800℃まで昇温し、この温度において3〜5時間維持する。この温度では木節粘土中の塩基、硝酸塩などがガス化し、植物由来の有機物の賦活化も開始する。
上記のガスは外部に放出されるため、図3及び図4に示すように連続細孔が形成される。また油分を含む水も侵入しやすい比較的大きめの穴も形成され、全体の表面積が大幅に増加する。
After that, the temperature is raised from about 600 ° C. to about 800 ° C. at a heating rate of 50 ° C./h, and the temperature is maintained at this temperature for 3 to 5 hours. At this temperature, bases, nitrates, etc. in the wood section clay are gasified, and activation of plant-derived organic matter is also started.
Since the above gas is released to the outside, continuous pores are formed as shown in FIGS. 3 and 4. In addition, relatively large holes that allow water containing oil to easily enter are also formed, which greatly increases the total surface area.

800℃からは100℃/hの昇温速度で昇温し、950℃付近から還元焼成の場合は空気量、ガス量を減らし、炉内を還元雰囲気とする。
このまま、昇温を継続して行くと、1050℃付近において、木節粘土及び植物(オガクズなどの有機物)の灰分が徐々にガラス化する。
The temperature is raised from 800 ° C. at a heating rate of 100 ° C./h, and in the case of reduction firing from around 950 ° C., the amount of air and gas is reduced to create a reducing atmosphere in the furnace.
If the temperature is continuously raised as it is, the ash content of the wood-knot clay and plants (organic matter such as sawdust) gradually vitrifies at around 1050 ° C.

ここで、上記の灰分中にはカルシウム(Ca)、マグネシウム(Mg)、カリウム(K)、リン(P)などと並んで、鉛(Pb)やカドミウム(Cd)、水銀(Hg)のような重金属が微量ではあるが含まれている。 Here, in the above ash content, along with calcium (Ca), magnesium (Mg), potassium (K), phosphorus (P), etc., lead (Pb), cadmium (Cd), mercury (Hg), etc. It contains a small amount of heavy metals.

また、ガラス化は灰分が溶け、結晶構造をとらずに流動性を持たない状態になる現象で、見かけは固体と同じだが、液体と同じように不規則な分子構造を持つ非結質(アモルファス)の状態となっている。 In addition, vitrification is a phenomenon in which ash melts and becomes non-fluid without taking a crystal structure. It looks the same as a solid, but is non-consolidated (amorphous) with an irregular molecular structure like a liquid. ).

上記のガラス化した層はガスが放出されたことによって形成された連続孔の表面に形成され、このガラス層には石英、粘土成分、アルミナ、金属(重金属)が融着する。これらの成分が融着することで、連続孔の表面は活性化(賦活化)され、連続孔の表面に接触した油分、汚染物質は分解される。
以下の表1は上記製法にて製造した浄化材の物性値を示す。
The vitrified layer is formed on the surface of continuous pores formed by the release of gas, and quartz, clay component, alumina, and metal (heavy metal) are fused to this glass layer. By fusing these components, the surface of the continuous pores is activated (activated), and oils and pollutants in contact with the surface of the continuous pores are decomposed.
Table 1 below shows the physical property values of the purifying material manufactured by the above manufacturing method.

Figure 2021037483
Figure 2021037483

図2は酸化焼成によって浄化材を製造する例を示しており、還元焼成と異なるのは、950℃付近から酸化状態のまま徐々に昇温し、最高到達温度を還元焼成よりも若干低い1250℃とした点である。 FIG. 2 shows an example of producing a purifying material by oxidative firing. The difference from reduction calcination is that the temperature is gradually raised from around 950 ° C in the oxidized state, and the maximum temperature reached is 1250 ° C, which is slightly lower than that of reduction calcination. It is a point that was made.

図3は本発明方法で製造した浄化材の写真、図4は同浄化材の拡大写真、図5は木節粘土のみを材料とし連続孔を形成するための有機物(オガクズなど)を混練しない比較例の拡大写真を示す。これらの写真から、オガクズなどの有機物を混練しない木節粘土のみでは、焼成後に陶磁器のように肌理が細かくなり水との接触面積が小さくなるが、オガクズなどの有機物を混練することで、連続気泡が形成され、水との接触面積が大きくなり且つ水中の油分子がトラップされることが分かる。 FIG. 3 is a photograph of the purifying material produced by the method of the present invention, FIG. 4 is an enlarged photograph of the purifying material, and FIG. An enlarged photograph of the example is shown. From these photographs, with only Kibushi clay, which does not knead organic matter such as sawdust, the texture becomes finer and the contact area with water becomes smaller like ceramics after firing, but by kneading organic matter such as sawdust, open cells Is formed, the contact area with water becomes large, and oil molecules in the water are trapped.

以下の表2は、本発明方法で製造した浄化材を用いてプロデュースウォータ(produced water)を浄化した場合の油分の減少割合(100ppmからの残留油分)を示したものであり、この表1から各種油分が大幅に除去(分解)されていることが分かる。 Table 2 below shows the rate of decrease in oil content (residual oil content from 100 ppm) when the produced water is purified using the purifying material produced by the method of the present invention. It can be seen that various oils have been significantly removed (decomposed).

Figure 2021037483
Figure 2021037483

また表3は、油分以外の汚染物質の除去率を示している。この表から、本発明方法で製造した浄化材は、油分だけでなく、重炭酸塩(Bicarbonate)、塩化物(Chloride)、硫酸塩(Sulfate)、ナトリウム(Sodium)、カルシウム(Calcium)、マグネシウム(Magnesium)、カリウム(Potassium)、バリウム(Barium)及びストロンチウム(Strontuim)が大幅に除去されることが判明した。 Table 3 shows the removal rate of pollutants other than oil. From this table, the purifying materials produced by the method of the present invention include not only oil but also bicarbonate (Bicarbonate), chloride (Chloride), sulfate (Sulfate), sodium (Sodium), calcium (Calcium), magnesium ( Magnesium), potassium (Potassium), barium (Barium) and strontuim (Strontuim) were found to be significantly removed.

Figure 2021037483
Figure 2021037483

本発明に係る製法で製造された浄化材は、プロデュースウォータに限らず、タンカーバラスト水、食品加工工場や化学工場の廃水、洗車排水、下水等の浄化に利用することができる。更に本発明方法で製造した浄化材はCOD、BODの数値を下げる効果も確認された。 The purifying material produced by the production method according to the present invention can be used not only for producing water but also for purifying tanker ballast water, wastewater of food processing factories and chemical factories, car wash wastewater, sewage and the like. Furthermore, it was confirmed that the purifying material produced by the method of the present invention has the effect of lowering the values of COD and BOD.

Claims (2)

以下の工程からなる水質浄化材の製造方法。
第1工程:木節粘土と植物由来の有機物とを水を加えて混錬して成形する。
第2工程:前記混錬した成形体を炉内にセットし、300℃以下で加熱し成形体中の水分を除去する。
第3工程:水分が除去された成形体を400〜500℃に保持し完全に炭化せしめる。
第4工程:焼成温度を750〜850℃まで上昇させ、この温度で温度を維持することで木節粘土中の塩基、硝酸塩をガス化せしめ、連続した細孔を形成する。
第5工程:1050℃まで昇温すると共に炉内環境を還元状態とし、前記連続した細孔表面をガラス化する。
第6工程:還元状態で1250〜1300℃まで昇温し、この温度を維持することで、ガラス化した部分に石英、アルミナ及び金属を溶着させ、細孔表面を賦活化する。
A method for manufacturing a water purification material consisting of the following steps.
First step: Kibushi clay and plant-derived organic matter are kneaded and molded by adding water.
Second step: The kneaded molded product is set in a furnace and heated at 300 ° C. or lower to remove water in the molded product.
Third step: The molded product from which water has been removed is held at 400 to 500 ° C. and completely carbonized.
Fourth step: The firing temperature is raised to 750 to 850 ° C., and the temperature is maintained at this temperature to gasify the bases and nitrates in the knot clay to form continuous pores.
Fifth step: The temperature is raised to 1050 ° C., the environment inside the furnace is reduced, and the continuous pore surface is vitrified.
Sixth step: The temperature is raised to 1.25 to 1300 ° C. in the reduced state, and by maintaining this temperature, quartz, alumina and metal are welded to the vitrified portion to activate the pore surface.
以下の工程からなる水質浄化材の製造方法。
第1工程:木節粘土と植物由来の有機物とを水を加えて混錬して成形する。
第2工程:前記混錬した成形体を炉内にセットし、300℃以下で加熱し成形体中の水分を除去する。
第3工程:水分が除去された成形体を400〜500℃に保持し完全に炭化せしめる。
第4工程:焼成温度を750〜850℃まで上昇させ、この温度で温度を維持することで木節粘土中の塩基、硝酸塩をガス化せしめ、連続した細孔を形成する。
第5工程:950℃まで炉内の酸化状態を維持したまま昇温することで前記連続した細孔表面をガラス化する。
第6工程:酸化状態で1200〜1300℃まで昇温し、この温度を維持することで、ガラス化した部分に石英、アルミナ及び金属を溶着させ、細孔表面を賦活化する。
A method for manufacturing a water purification material consisting of the following steps.
First step: Kibushi clay and plant-derived organic matter are kneaded and molded by adding water.
Second step: The kneaded molded product is set in a furnace and heated at 300 ° C. or lower to remove water in the molded product.
Third step: The molded product from which water has been removed is held at 400 to 500 ° C. and completely carbonized.
Fourth step: The firing temperature is raised to 750 to 850 ° C., and the temperature is maintained at this temperature to gasify the bases and nitrates in the knot clay to form continuous pores.
Fifth step: The continuous pore surface is vitrified by raising the temperature to 950 ° C. while maintaining the oxidized state in the furnace.
Sixth step: The temperature is raised to 1200 to 1300 ° C. in an oxidized state, and by maintaining this temperature, quartz, alumina, and a metal are welded to the vitrified portion to activate the pore surface.
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Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5256093A (en) * 1976-09-20 1977-05-09 Kato Toshiya Manufacture of catalysts for exhaust water purification
JPS557549A (en) * 1978-06-30 1980-01-19 Kouzou Shibata Porous article and its manufacture and use
JPS57118062A (en) * 1981-01-13 1982-07-22 Kawasaki Itsuhiro Manufacture of water-containing ceramic
JPS59156481A (en) * 1983-02-26 1984-09-05 Satoru Imamura Advanced purification of waste water from living system
JPS61291473A (en) * 1985-06-19 1986-12-22 フイルトンインタ−ナシヨナル株式会社 Manufacture of porous ceramics
US4652376A (en) * 1983-03-10 1987-03-24 Filton International Co. Method for disposing emulsifiable oil-containing waste water
JPH10101452A (en) * 1996-09-20 1998-04-21 Shunichi Kumaoka Porous ceramic having amorphous pore surface and its production
JPH10118643A (en) * 1996-10-22 1998-05-12 Shunichi Kumaoka Method for treating waste solution-waste water containing organochlorine compound and apparatus therefor
JP2000154073A (en) * 1998-11-17 2000-06-06 Noboru Ishibashi Production of porous fired body
JP2001048636A (en) * 1999-08-17 2001-02-20 Maruishi Yogyo Genryo Kk Production of ceramics utilizing microorganism
JP2002097084A (en) * 2000-09-19 2002-04-02 National Institute Of Advanced Industrial & Technology Method of manufacturing microporous ceramic and method of utilization of the same

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5256093A (en) * 1976-09-20 1977-05-09 Kato Toshiya Manufacture of catalysts for exhaust water purification
JPS557549A (en) * 1978-06-30 1980-01-19 Kouzou Shibata Porous article and its manufacture and use
JPS57118062A (en) * 1981-01-13 1982-07-22 Kawasaki Itsuhiro Manufacture of water-containing ceramic
JPS59156481A (en) * 1983-02-26 1984-09-05 Satoru Imamura Advanced purification of waste water from living system
US4652376A (en) * 1983-03-10 1987-03-24 Filton International Co. Method for disposing emulsifiable oil-containing waste water
JPS61291473A (en) * 1985-06-19 1986-12-22 フイルトンインタ−ナシヨナル株式会社 Manufacture of porous ceramics
JPH10101452A (en) * 1996-09-20 1998-04-21 Shunichi Kumaoka Porous ceramic having amorphous pore surface and its production
JPH10118643A (en) * 1996-10-22 1998-05-12 Shunichi Kumaoka Method for treating waste solution-waste water containing organochlorine compound and apparatus therefor
JP2000154073A (en) * 1998-11-17 2000-06-06 Noboru Ishibashi Production of porous fired body
JP2001048636A (en) * 1999-08-17 2001-02-20 Maruishi Yogyo Genryo Kk Production of ceramics utilizing microorganism
JP2002097084A (en) * 2000-09-19 2002-04-02 National Institute Of Advanced Industrial & Technology Method of manufacturing microporous ceramic and method of utilization of the same

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