JPH02221150A - Water purifying material and its production - Google Patents
Water purifying material and its productionInfo
- Publication number
- JPH02221150A JPH02221150A JP1041018A JP4101889A JPH02221150A JP H02221150 A JPH02221150 A JP H02221150A JP 1041018 A JP1041018 A JP 1041018A JP 4101889 A JP4101889 A JP 4101889A JP H02221150 A JPH02221150 A JP H02221150A
- Authority
- JP
- Japan
- Prior art keywords
- water
- purification material
- topsoil
- purifying material
- shale
- 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.)
- Pending
Links
- 239000000463 material Substances 0.000 title claims abstract description 36
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 29
- 238000004519 manufacturing process Methods 0.000 title claims description 4
- 239000011230 binding agent Substances 0.000 claims abstract description 10
- 238000000746 purification Methods 0.000 claims description 29
- 239000000126 substance Substances 0.000 claims description 7
- 238000010304 firing Methods 0.000 claims description 3
- 244000005700 microbiome Species 0.000 abstract description 6
- BPQQTUXANYXVAA-UHFFFAOYSA-N Orthosilicate Chemical compound [O-][Si]([O-])([O-])[O-] BPQQTUXANYXVAA-UHFFFAOYSA-N 0.000 abstract description 4
- 229910001653 ettringite Inorganic materials 0.000 abstract description 4
- 239000000203 mixture Substances 0.000 abstract description 4
- 239000004927 clay Substances 0.000 abstract description 2
- 239000010865 sewage Substances 0.000 description 7
- 230000000694 effects Effects 0.000 description 4
- 238000005469 granulation Methods 0.000 description 4
- 230000003179 granulation Effects 0.000 description 4
- 229910052760 oxygen Inorganic materials 0.000 description 4
- 239000008213 purified water Substances 0.000 description 4
- 239000004575 stone Substances 0.000 description 4
- IMROMDMJAWUWLK-UHFFFAOYSA-N Ethenol Chemical compound OC=C IMROMDMJAWUWLK-UHFFFAOYSA-N 0.000 description 3
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 3
- 230000005484 gravity Effects 0.000 description 3
- 238000000034 method Methods 0.000 description 3
- 229920002451 polyvinyl alcohol Polymers 0.000 description 3
- 238000004140 cleaning Methods 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 238000007667 floating Methods 0.000 description 2
- 239000010438 granite Substances 0.000 description 2
- 239000008187 granular material Substances 0.000 description 2
- 229910010272 inorganic material Inorganic materials 0.000 description 2
- 239000011147 inorganic material Substances 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 102000004169 proteins and genes Human genes 0.000 description 2
- 108090000623 proteins and genes Proteins 0.000 description 2
- 239000002893 slag Substances 0.000 description 2
- -1 Ceracola Substances 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 102100027340 Slit homolog 2 protein Human genes 0.000 description 1
- 101710133576 Slit homolog 2 protein Proteins 0.000 description 1
- 229920002472 Starch Polymers 0.000 description 1
- 240000006909 Tilia x europaea Species 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 235000014633 carbohydrates Nutrition 0.000 description 1
- 150000001720 carbohydrates Chemical class 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 229910010293 ceramic material Inorganic materials 0.000 description 1
- 239000011538 cleaning material Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000005187 foaming Methods 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 150000002632 lipids Chemical class 0.000 description 1
- 229920000609 methyl cellulose Polymers 0.000 description 1
- 239000001923 methylcellulose Substances 0.000 description 1
- 102000039446 nucleic acids Human genes 0.000 description 1
- 108020004707 nucleic acids Proteins 0.000 description 1
- 150000007523 nucleic acids Chemical class 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 239000011435 rock Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 235000019698 starch Nutrition 0.000 description 1
- 239000008107 starch Substances 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
及びその水浄化材料を用いた水浄化材の製造方法に関す
る。DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field] The present invention relates to a method for producing a water purification material using the water purification material.
従来より汚水の浄化法として、玉石を充填した浄化槽に
汚水を尋人し、玉石の表面に生息する微生物に汚水中の
汚物、炭水化物、脂質及び蛋白質等を喰わせて浄化する
方法が実施されていた。Conventionally, the method of purifying sewage has been to pour the sewage into a septic tank filled with cobblestones, and have the microorganisms that live on the surface of the cobblestones consume the filth, carbohydrates, lipids, and proteins in the sewage to purify it. Ta.
しかしながら、近年河川の上流にダムが建設されたため
、下流の河川敷などに、水浄化材として適した粒度や形
状の玉石が不足していること。また、河川敷における玉
石の採集が禁止されたこと。However, in recent years, as dams have been constructed upstream of rivers, there is a shortage of cobblestones of suitable particle size and shape as water purification materials in downstream riverbeds. In addition, collecting cobblestones from riverbeds was prohibited.
などにより、玉石を使用した大規模な浄化槽を設置する
のに苦慮しているのが現状である。そしてこの玉石の不
足を補うために、花こう岩や凝灰岩など砕いて玉石の代
わりに使用する方法や高炉スラグ砕石を使用する方法な
どが提案されている(技術資料、昭和66年昭朱興産(
株)発行)。For these reasons, it is currently difficult to install large-scale septic tanks using cobblestones. In order to compensate for this shortage of cobblestone, methods have been proposed such as using crushed granite or tuff instead of cobblestone, and using crushed blast furnace slag (technical data, 1988 Shu Kosan).
(Issued by).
しかしながら、仁れら天然砕石や高炉スラグ砕石は玉石
と比べ過度の凹凸があるため、微生物の付着は良好であ
るが、砕石に付着した汚泥を清水で洗浄しても、付着し
た汚泥は完全に除去されず表向に溜りやすく、短期間で
目づまりを起し、浄化の目的が達せられなくなるa題が
あつ友。However, since natural crushed stone and blast furnace slag crushed stone have excessive irregularities compared to cobblestone, microorganisms can easily adhere to them. A problem with this problem is that it is not removed and tends to accumulate on the surface, causing clogging in a short period of time, making it impossible to achieve the purpose of purification.
本発明者らは、特定の材料t−用いることにより微生物
が生息するのに最も適した水浄化材が得られる知見を得
て、本発明を完成するに至った。The present inventors have completed the present invention based on the knowledge that a water purification material most suitable for microorganisms to live in can be obtained by using a specific material.
即ち、本発明は、表土、リパライト、頁岩及びエトリン
がイト生成物からなる群↓り選ばれた一種又は二種以上
の無機物と有機バインダーとを主成分とする水浄化材料
であり、更に、それを用いた水浄化材の製造方法である
。That is, the present invention is a water purification material whose main components are one or more inorganic substances selected from the group consisting of topsoil, lipalite, shale, and ethrine products, and an organic binder; This is a method for producing a water purification material using.
以下、本発明yk評しく説明する。The present invention will be explained in detail below.
本発明における無機物とは表土、リパライト、頁岩及び
エトリンがイト生成物からなる群より選ばれた一種又は
二a以上である。In the present invention, the inorganic substance is one or more selected from the group consisting of topsoil, lipalite, shale, and ethlinite products.
本発明で使用する表土とは、地殻の表面又は比較的浅い
部分に存在する含水アルミナ賀のケイ酸塩である。The topsoil used in the present invention is a hydrated alumina silicate that exists on the surface of the earth's crust or in a relatively shallow part.
また、リパライトとは、天然に存在する微細なアルミナ
ケイ酸塩を主成分とする生状の混合物である。Moreover, lipalite is a raw mixture whose main component is naturally occurring fine alumina silicate.
また、真岩とは層状に固化した粘土で発泡作用を持つも
のである。In addition, true rock is clay that has solidified into layers and has a foaming effect.
更に、エトリンガイト生厄物とは、エトリンがイト及び
エトリンがイトを生成するもので、例えば、3CaO’
AJ203”3CaSOa ”32H20、各種セメン
ト、セラコラ、石灰類及びアルミナ質原料等が挙げられ
る。Furthermore, ettringite nuisances are those that produce ettrin and ettringite, such as 3CaO'
Examples include AJ203"3CaSOa"32H20, various cements, Ceracola, limes, and alumina raw materials.
無機物の粒度は300μ以下が好ましい。300μを越
えると造粒する際に水浄化材(以下浄化材という)の形
状の制御が困難になる。The particle size of the inorganic material is preferably 300 μm or less. If it exceeds 300μ, it becomes difficult to control the shape of the water purification material (hereinafter referred to as the purification material) during granulation.
本発明で使用する有機バインダーとは、ポバール、メチ
ルセルロース、デンプン、m、蛋白質、脂肪及び核酸等
をいい、このうちの−樵又は二極以上が使用できる。The organic binder used in the present invention refers to poval, methylcellulose, starch, protein, fat, nucleic acid, etc., and among these, one or more can be used.
有機バインダーの使用誓は、無機物100fi−振部に
対して、2ON、置部以下が好ましい。有機バインダー
の使用址を変化させることによって、造粒し、焼成して
できる浄化材の気孔率や比N等を過当に制御することが
できるが、20m1t部ケ越えて使用するとその制御が
困難になりやすい。気孔率が大きいと比重は下がり、浄
化効果が上昇する。It is preferable that the organic binder should be used in a range of 2ON or less per 100 parts of the inorganic material. By changing the usage area of the organic binder, it is possible to excessively control the porosity, ratio N, etc. of the purification material produced by granulation and firing, but it becomes difficult to control this when used in excess of 20 m/t. Prone. If the porosity is large, the specific gravity will decrease and the purification effect will increase.
前述の無機物と自機バインダーを主成分とする水浄化材
料(以下浄化材料という)と水とを混合して造粒する。A water purification material (hereinafter referred to as purification material) containing the above-mentioned inorganic substance and organic binder as main components is mixed with water and granulated.
水の使用箪は、無機物と有機バインダーの合計並100
重量部に対し、401量部以下が好ましい。40重葉部
を越えると造粒が困難になりやす造粒条件Vi特に制限
されるものではな(・。通常パン型造粒機やハイスピー
ドミキサーなどで造粒し、その後焼成する。The amount of water used is 100% of the total amount of inorganic and organic binders.
The amount is preferably 401 parts by weight or less. If the weight exceeds 40, granulation tends to become difficult.The granulation conditions Vi are not particularly limited (・) Granules are usually granulated using a pan-type granulator, high-speed mixer, etc., and then baked.
焼成は通常電気炉やキルン等を用いて1.00000以
上の高温で焼成する。Firing is usually performed at a high temperature of 1.00000°C or higher using an electric furnace, kiln, or the like.
造粒し、焼成した浄化材の大きさは、径6〜60鶴が好
ましい。3鶴未満では、浄化水の流水性が悪化し、60
酊を越えると浄化能力が低下する傾向がある。The size of the granulated and fired purifying material is preferably 6 to 60 mm in diameter. If it is less than 3 cranes, the flowability of purified water will deteriorate and the water will reach 60
If you exceed the level of inebriation, your purifying ability tends to decline.
また、浄化材の形状はできるだけ真球状にして六面積を
大きくすることが、浄化能力向上の而か以上のように製
造した浄化材を従来の玉石の代りに使用し、浄化槽を造
ると、汚水の浄化に当り、微生物の付着が良好になり、
浄化速度が大になって浄化効率が向上するばかりでなく
、浄化材を洗浄する際、玉石の比重1.5〜2.0に比
べ浄化材の比重が0.9〜1.1と小さいため、洗浄水
により浮遊運動し、浄化材間の互祿作用により、浄化材
界面から付着した汚泥が除去され易くなるので、洗浄時
m]は短#iされ、浄化材を長時1”a1繰り返し使用
することができる。In addition, making the shape of the purification material as true spherical as possible and increasing its area will improve the purification ability.If the purification material manufactured as described above is used in place of the conventional boulders and a septic tank is built, the sewage When cleaning, the adhesion of microorganisms becomes better,
Not only does the purification speed increase and purification efficiency improve, but when cleaning the purification material, the specific gravity of the purification material is 0.9 to 1.1, which is smaller than the specific gravity of cobblestone, which is 1.5 to 2.0. , due to the floating movement caused by the washing water and the interaction between the purifying materials, the sludge attached to the surface of the purifying materials is easily removed. can be used.
本発明の浄化材Vi1.OOO’C以上の同温で焼成し
たセラミック實であるため、非常に硬く丈夫であり、浄
化材の洗浄は何回も可能である。更に、有害な物質の浴
出は全くなく、均一化しているため、充填が適当であり
、浄化水の通過が全般にわたって平均して流れ、@九を
おこさない。従って、有効接触面積か天然の玉石や砕石
に比べて恋しく大きいため、その分、浄化槽が小烙くて
す2経済的である。Purification material of the present invention Vi1. Since it is a ceramic material fired at the same temperature of OOO'C or higher, it is extremely hard and durable, and the purifying material can be washed many times. In addition, there is no leaching of harmful substances, and since it is uniform, the filling is appropriate, and the passage of purified water flows evenly over the entire area, and does not cause @9. Therefore, since the effective contact area is larger than that of natural cobblestone or crushed stone, the septic tank is less expensive and more economical.
〔実施例〕 以下、実施例によって、本発明を更に拝しく祝明する。〔Example〕 Hereinafter, the present invention will be further illustrated with reference to Examples.
実施例1
無機物として新潟県西頚部黒姫山産の地±100m1H
1tBと、有機バインダーとして電気化学工業(株)の
ポバール商品名[デンカポバールに17SBJ2.51
1m部を混合した。この混合物に表土100N11部に
対して201[(Ji部の水を加えつつ造粒して球状体
を造り、電気炉を用い、1,300℃の烏温で1時間焼
成し5〜105mの浄化材とした。Example 1 As an inorganic substance, a site from Mt.
1 tB, and Denka Kagaku Kogyo Co., Ltd.'s Poval product name [Denka Poval 17SBJ2.51] as an organic binder.
1 m part was mixed. To this mixture, granules were made by adding 201 [(Ji part) of water to 11 parts of topsoil to form a spherical body, which was then fired in an electric furnace at a temperature of 1,300°C for 1 hour to purify 5 to 105 m. It was used as a material.
図−1に示す50X50X100(σ)の実験用の浄化
槽1内のスリット2の上に、浄化材3を空隙率が約20
容t%になるように充填した。浄化11の上部に設けた
汚水の汚水1t4からB、O,D。The purifying material 3 is placed over the slit 2 in the experimental septic tank 1 of 50 x 50 x 100 (σ) shown in Figure 1 with a porosity of approximately 20.
It was filled to a volume of t%. B, O, D from 1t4 of sewage installed at the top of purification 11.
(生物化学的酸素装求*)35W/l及びS、S。(Biochemical oxygen demand*) 35 W/l and S, S.
(浮遊性固形物質)50w/l含有の汚水(20’c
)を流速0.8〜8.01 /分で導入し、圧縮空気を
空気管5より181/分の割合で吹込み、浄化水を排水
管6から排出した。尚、浄化材は予め汚水中の微生物を
足場したものを用いた。浄化槽1の下部に設け7’(消
水尋入管7から清水を導入し、浄化材の狭面を洗浄した
。浄化材の代わシに花こう岩砕石及び玉石を用いて同様
の実験を行った。(Floating solids) Sewage containing 50w/l (20'c
) was introduced at a flow rate of 0.8 to 8.01/min, compressed air was blown in from the air pipe 5 at a rate of 181/min, and purified water was discharged from the drain pipe 6. Note that the purification material used was one in which microorganisms in wastewater were scaffolded in advance. Clean water was introduced from the septic tank 7 installed at the bottom of the septic tank 1 to clean the narrow side of the purification material.A similar experiment was conducted using crushed granite and cobblestone instead of the purification material. .
その結果を衣−1及び表−2に示す。The results are shown in Cloth-1 and Table-2.
以上の結果、本発明の浄化材を使用しfc場合のB、O
,D、の除去率は滞留時間が2時間和度で90峰となり
、砕石や玉石に比べ1.5倍程度向上していることがわ
かる。ま7t、s、s、除去率は滞留時間が2時間和度
ではほぼ100%となり、砕石や玉石に比べ1.3倍程
度向上していることがわかる。As a result of the above, B, O
It can be seen that the removal rate of . It can be seen that the removal rate is almost 100% when the residence time is 2 hours, which is about 1.3 times better than crushed stone or cobblestone.
実施例2
無機物として衣−6に示すものを使用したこと以外は実
施9′l11と同様に行った。結果を衣−4及び衣−5
に示す。Example 2 The same procedure as in Example 9'l11 was carried out except that the inorganic substance shown in Cloth-6 was used. The result is Cloth-4 and Cloth-5
Shown below.
氏−6 発明の効果〕 本発明の浄化材を使用すれば下記の効果がある。Mr.-6 Effect of the invention〕 Use of the purifying material of the present invention provides the following effects.
)1,000℃以工の高温で焼成したセラミックス質で
あるため、非常に硬く丈夫であり、浄化材の洗浄が伺回
も可能である。) Since it is made of ceramic fired at a high temperature of 1,000°C or higher, it is extremely hard and durable, and the cleaning material can be washed repeatedly.
)均一化しているため、浄化水の通過が全般にわたって
平均して流れ、−流をおこさない。) Since it is uniform, the purified water flows evenly over the entire area and does not cause any negative flow.
)有効接触面積が大きく、その分、浄化槽を小さくでき
、経済的である。) The effective contact area is large, and the septic tank can be made smaller accordingly, making it economical.
) B、O,D、除去率、S、S、除去率を著しく高
くすることができる。) B, O, D, removal rate, S, S, removal rate can be significantly increased.
面の簡単な説明 図−1は、浄化槽の断面図である。Brief description of the surface Figure 1 is a sectional view of the septic tank.
号
1・・・浄化槽、 2・・・スリット、3・・
・浄化材、 4・・・汚水管、5・・・空気管
、 6・・・排水管、T・・・清水導入管。No. 1...Septic tank, 2...Slit, 3...
・Purification material, 4... Sewage pipe, 5... Air pipe, 6... Drain pipe, T... Fresh water introduction pipe.
特許出願人 電気化学工条株式公社Patent applicant: Denki Kagaku Kojo Co., Ltd.
Claims (2)
物からなる群より選ばれた一種又は二種以上の無機物と
有機バインダーとを主成分とする水浄化材料。(1) A water purification material whose main components are one or more inorganic substances selected from the group consisting of topsoil, lipalite, shale, and ethrine-based products, and an organic binder.
し、焼成することを特徴とする水浄化材の製造方法。(2) A method for producing a water purification material, which comprises mixing the water purification material according to claim 1 with water, granulating it, and firing it.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1041018A JPH02221150A (en) | 1989-02-21 | 1989-02-21 | Water purifying material and its production |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1041018A JPH02221150A (en) | 1989-02-21 | 1989-02-21 | Water purifying material and its production |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH02221150A true JPH02221150A (en) | 1990-09-04 |
Family
ID=12596654
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP1041018A Pending JPH02221150A (en) | 1989-02-21 | 1989-02-21 | Water purifying material and its production |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH02221150A (en) |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS61174178A (en) * | 1985-01-25 | 1986-08-05 | 島崎 福教 | Soft ceramic sintered body and manufacture |
JPS62167268A (en) * | 1986-01-17 | 1987-07-23 | 工業技術院長 | Microbe fixing carrier |
JPS647996A (en) * | 1987-06-30 | 1989-01-11 | Iwao Jiki Kogyo | Rotary plate body for waste water treatment |
-
1989
- 1989-02-21 JP JP1041018A patent/JPH02221150A/en active Pending
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS61174178A (en) * | 1985-01-25 | 1986-08-05 | 島崎 福教 | Soft ceramic sintered body and manufacture |
JPS62167268A (en) * | 1986-01-17 | 1987-07-23 | 工業技術院長 | Microbe fixing carrier |
JPS647996A (en) * | 1987-06-30 | 1989-01-11 | Iwao Jiki Kogyo | Rotary plate body for waste water treatment |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP2009517327A5 (en) | ||
JP4540656B2 (en) | Composition for porous ceramics, porous ceramics using the same, and method for producing the same | |
JP2008263928A (en) | Dredged soil block for installing beach bedrock | |
CN106747558A (en) | A kind of micro porous filtration purification stone and preparation method thereof | |
CN112624644A (en) | Preparation method of functionally gradient sludge ecological artificial sandstone | |
JPH02221150A (en) | Water purifying material and its production | |
JPS594493A (en) | Medium for cleaning up sewage by contact oxidation | |
CN1238275C (en) | Filter material having phosphor adsorbing and biological membrane function and its preparing method | |
CN109110929B (en) | Water purification biological material and preparation method thereof | |
JP2004024204A (en) | Method for improving environment in water or on beach and environment improving material | |
JPH11188377A (en) | Water quality clarification porous concrete member for denitrification | |
JP2000070960A (en) | Dephosphorization material produced by utilizing building waste | |
JPH0929293A (en) | Treatment of bottom deposit in lake and marsh or the like | |
TWI364408B (en) | A method for sintering aggregates from wasted sludge | |
CN110204053A (en) | A kind of efficient dephosphorization Wetland Substrate of wetland engineering and preparation method thereof | |
JP4774012B2 (en) | Scum generation suppression method | |
KR100818547B1 (en) | Tidal Flat Purifying Agent | |
JP4645195B2 (en) | Method for producing carbonated solid | |
JPS60143896A (en) | Purifying medium by contact oxidation of filthy water | |
JP2003103285A (en) | Water cleaning porous body | |
JP3338414B2 (en) | Sashimi block with water purification ability | |
JPH08276198A (en) | River purifying apparatus | |
SU738638A1 (en) | Method of cleaning water by filtering | |
JPH06101352A (en) | Method of treating porous material, cracked surface | |
JP2005006598A (en) | Artificial sand for raising shellfish and method for producing the same |