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JPS5822246B2 - High exhaustion - Google Patents
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JPS5822246B2 - High exhaustion - Google Patents

High exhaustion

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Publication number
JPS5822246B2
JPS5822246B2 JP50103465A JP10346575A JPS5822246B2 JP S5822246 B2 JPS5822246 B2 JP S5822246B2 JP 50103465 A JP50103465 A JP 50103465A JP 10346575 A JP10346575 A JP 10346575A JP S5822246 B2 JPS5822246 B2 JP S5822246B2
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JP
Japan
Prior art keywords
medium
waste liquid
ppm
separation
minutes
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
JP50103465A
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Japanese (ja)
Other versions
JPS5227077A (en
Inventor
今村哲
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Individual
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Individual
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Priority to JP50103465A priority Critical patent/JPS5822246B2/en
Publication of JPS5227077A publication Critical patent/JPS5227077A/en
Publication of JPS5822246B2 publication Critical patent/JPS5822246B2/en
Expired legal-status Critical Current

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  • Compositions Of Oxide Ceramics (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Catalysts (AREA)
  • Treating Waste Gases (AREA)
  • Gas Separation By Absorption (AREA)
  • Water Treatment By Sorption (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Description

【発明の詳細な説明】 力n工工場より排出される廃液及び排出ガスはその中に
含まれる夫々の物質によって汚染の原因となっているが
、それらを除去するためには従来凝。
DETAILED DESCRIPTION OF THE INVENTION Waste liquid and exhaust gas discharged from a power plant are a cause of pollution due to the substances contained therein, and conventional coagulation methods have been used to remove them.

乗法、吸着法、活性汚泥法、触媒法等が行なわれている
Multiplicative methods, adsorption methods, activated sludge methods, catalyst methods, etc. are used.

しかしながら、例えば凝集法では凝集剤を使用すること
で凝集物の増加をきたすし、吸着法では吸着剤の取扱い
の難しさとか、その効力の持続性。
However, for example, in the flocculation method, the use of a flocculant causes an increase in aggregates, and in the adsorption method, there are problems such as the difficulty of handling the adsorbent and the sustainability of its effectiveness.

の問題等があった。There were some problems.

本件発明は、ただ接触させるだけで、これらの汚染物質
の除去が有効かつ能率的に行なえる新しい合成媒体を提
供するものである。
The present invention provides a new synthesis medium that can effectively and efficiently remove these contaminants simply by contacting them.

すなわち、この媒体はα)カオリナイト、加水ハロサイ
ト等のA/203含量の多い粘土、(2)石灰岩及び石
灰岩ドロマイト等のCaCO3含量の多い岩石、(3)
Si02を生成分とし、それに微量のFe2O3、Fe
d、に20.Na2O、MgO,チタン等を含む火山灰
(熔岩粉末)の三種類の土石の粉末を等量又はそれに近
い割合で混合し、加水後良く練り込み成型して自然乾燥
又は赤外線乾燥にて充分乾燥した後、焼成炉に於いて1
000℃前後の高温で焼成したものである。
That is, this medium is α) clay with high A/203 content such as kaolinite and hydrated hallosite, (2) rock with high CaCO3 content such as limestone and limestone dolomite, (3)
Si02 is the generated component, and trace amounts of Fe2O3 and Fe
d, to 20. Three types of soil and stone powders, including volcanic ash (lava powder) containing Na2O, MgO, titanium, etc., are mixed in equal or close proportions, and after adding water, knead well and mold, and dry thoroughly by natural drying or infrared drying. , in the firing furnace 1
It is fired at a high temperature of around 000°C.

勿論、天然に産出するある種の岩石類が液体の精製の際
の涙過助剤として用いられることは知られており、更に
例えば特公昭30−1538号公報にも記載されている
ように、これらの天然物には粘土等の如き液温性解膠物
質又は石灰、マグネシア、その他アルカリ金属塩等の如
き易溶性物質が含まれ、これらの物質は沖過の際の障碍
になるので焙焼等により不溶性化する方法もとられてい
たが、満足な結果はえられず、きわめて良質な材料を用
い常温又は加熱(中温)下に濃厚状態においてアルカリ
石鹸溶液を添加混捏し、次いで硫酸骨上溶液を添加混捏
し乾燥粉砕することにより漸く粘稠液体の濾過用といっ
た限られた用途に適するものをえていたにすぎない。
Of course, it is known that certain types of naturally occurring rocks are used as lachrymal aids in the purification of liquids, and as described in Japanese Patent Publication No. 30-1538, These natural products include liquid-temperature peptizing substances such as clay, or easily soluble substances such as lime, magnesia, and other alkali metal salts. A method of making it insoluble was also used, but no satisfactory results were obtained, so using very high quality materials, adding and kneading an alkaline soap solution in a concentrated state at room temperature or heating (medium temperature), then adding sulfuric acid to the bone and kneading it. By adding, kneading, drying and pulverizing the solution, a product suitable for limited uses such as filtration of viscous liquids was finally obtained.

しかしながら、本件発明者は、これらの天然土石中特定
の三種類を選びほぼ等量あて混練し、高温(1000°
C前後)で焼成する簡単な方法により、それぞれのもつ
欠点も逆に生かして多目的、多用途用に適したものをは
じめて得ることができ、とくに種々の物質を含む廃液や
排出ガスの脱色浄化に画期的な性能を発揮する本件合成
媒体の発明に至ったのである。
However, the present inventor selected three specific types of these natural stones, kneaded them in approximately equal amounts, and heated them at a high temperature (1000°C).
By using a simple method of firing with (before and after C), it is possible to take advantage of the drawbacks of each and obtain for the first time a product suitable for multiple purposes, especially for decolorizing and purifying waste liquids and exhaust gases containing various substances. This led to the invention of the subject synthetic medium that exhibits groundbreaking performance.

成分中粘土及び火山灰は固型化と堅牢性を与え、また石
灰岩はCO2のガス化によって焼成物中に多気孔性を与
える。
Clay and volcanic ash in the ingredients provide solidification and robustness, and limestone provides porosity in the fired product through gasification of CO2.

しかしこの石灰岩は、混合比が上記配合比を上回るとシ
リカ、アルミナ等に対する融合過剰により、製品は空気
中の炭酸ガスを吸収し炭酸カルシウムとなり劣化現象を
おこすから注意を要する。
However, with this limestone, care must be taken because if the mixing ratio exceeds the above-mentioned mixing ratio, excessive fusion of silica, alumina, etc. will cause the product to absorb carbon dioxide gas in the air and turn into calcium carbonate, causing deterioration.

また、焼成温度を1000°C前後としたのは、火山灰
の融解温度がそれぞれ約960℃及び約1100℃であ
ることから、混合土石を充分融解結合させるためである
Furthermore, the firing temperature was set at around 1000°C in order to sufficiently melt and bond the mixed earth and stone since the melting temperatures of volcanic ash are about 960°C and about 1100°C, respectively.

かくして、この媒体はAl2O3による吸着性、CaO
によるイオン性、5i02の焼成時における化学作用に
よる触媒性をも備えるものである。
Thus, this medium has adsorption properties due to Al2O3, CaO
It also has ionic properties due to 5i02 and catalytic properties due to chemical action during calcination of 5i02.

また熱伝導性もあって、この性質により陶磁器にみられ
る断熱性を解消し媒体老廃後の再生時におげろ熱効率を
高めることができる。
It also has thermal conductivity, which eliminates the heat insulating properties found in ceramics and improves thermal efficiency when regenerating media after it is used up.

なお、上記したとおり各種成分の中、混合比としてCa
CO3が焼成後媒体に対し劣化現象をおこす混合比であ
ってはならないから、この成分は、媒体全体の20係前
後を限度とすべきである。
As mentioned above, among the various components, the mixing ratio of Ca
Since the mixing ratio of CO3 should not cause deterioration of the medium after firing, the content of this component should be limited to around 20 parts of the entire medium.

以上の諸性質によりこの媒体は前述のようにこれを単に
接触させるだけで汚染物質を分離させ、たとえば分離す
るSSO量等は凝集法によるそれとは比較にならない。
Due to the above-mentioned properties, this medium separates contaminants simply by contacting it as described above, and the amount of SSO separated, for example, is incomparable to that obtained by the flocculation method.

そして使用時の沈澱物の量は極めて少(、分離沈澱物の
除去のための機械的規模も小さくて済むことにもなる。
Further, the amount of precipitate during use is extremely small (and the mechanical scale for removing the separated precipitate can also be small).

更、排出物によっては媒体に接触させる前に色色の目的
に応じて廃液中に例えば硫酸骨上、醋酸、塩酸、硫酸鉄
等の促進剤を極微量与えることにより急速な反応で分離
現象を起させることもでき、また加熱により再生使用の
できるものであるが、接触時の震動付与でその持続性を
高めることも可能である。
Furthermore, depending on the waste, a very small amount of an accelerator such as sulfuric acid, acetic acid, hydrochloric acid, iron sulfate, etc. can be added to the waste liquid depending on the purpose of its color before contact with the medium, causing a rapid reaction to occur. It is also possible to reuse it by heating it, but it is also possible to increase its durability by applying vibration when it comes into contact.

以下実施例により具体的に説明する。This will be explained in detail below using examples.

実施例 カオリナイ)(A/203含量の多い粘土)として鹿児
島県産の入来カオリン(成分比二5i0254.15係
、A120330.60%、N201.80係、Fe2
031.21%、Mg00.25%、K2O0,20係
、Ca00.03 %、水分その他11.76 % )
(7)粉末1.1 kQに、大理石粉末1kgと火山
灰として鹿児島県産のシラス(成分比: 5iQ270
.54係、At20,13.10係、K2O3,60係
、N2O2,95%、Fe2032.32 %、Mg0
0.48%、チタン、水分その他7.01 % ) 1
kt)を加え、水分を与えて攪拌後取出し、真空土練
機で混練したうえ直径IQff*、20mmの球形及び
直径40mm長さ45朋の円筒形に成型乾燥し、100
0℃で8時間焼成し媒体を得た。
Example kaolin) (clay with high A/203 content) was imported kaolin from Kagoshima Prefecture (component ratio 25i0254.15, A120330.60%, N201.80, Fe2
031.21%, Mg00.25%, K2O0.20%, Ca00.03%, water and other 11.76%)
(7) 1.1 kQ of powder, 1 kg of marble powder and whitebait from Kagoshima prefecture as volcanic ash (component ratio: 5iQ270
.. 54 section, At20, 13.10 section, K2O3, 60 section, N2O2, 95%, Fe2032.32%, Mg0
0.48%, titanium, water and other 7.01%) 1
kt), added moisture, stirred, taken out, kneaded in a vacuum clay kneader, molded into a sphere with a diameter IQff* of 20 mm and a cylindrical shape with a diameter of 40 mm and a length of 45 mm, and dried.
A medium was obtained by firing at 0° C. for 8 hours.

生成媒体の成分比は ’ SiQ、 52.26 % CaO21,
50%A/20318.24係 Fe2O32,51
係Mg0 2.41係 K2O1,62係N20
1.26係 その他 0.2 係であった。
The composition ratio of the generation medium is 'SiQ, 52.26% CaO21,
50%A/20318.24 Section Fe2O32,51
Mg0 2.41 K2O1, 62 N20
1.26 Section Others 0.2 Section.

この媒体の使用例を示すと次のとおりであった。Examples of how this medium was used were as follows.

1)直径10朋の球形に成型焼成した媒体を2e容量シ
リンダーの中に1.61充填し、染料廃液21に適用し
た結果は、15分後に反応開始し、染色剤の分離と共に
沈澱脱色が行なわれ、30分後には極く微かな色度を残
すのみとなり、1時間で分離は完了した。
1) A 2e capacity cylinder was filled with 1.61 liters of the medium formed into a spherical shape with a diameter of 10 mm and applied to the dye waste liquid 21. The reaction started after 15 minutes, and precipitation and decolorization occurred along with separation of the dyeing agent. After 30 minutes, only a very faint chromaticity remained, and the separation was completed in 1 hour.

この廃液はBOD1900ppm 透視度0度であった
が処理後はBol)357ppm 透視度28度、BO
D除去率であった。
This waste liquid had a BOD of 1900 ppm and a transparency of 0 degrees, but after treatment it had a BOD of 357 ppm, a transparency of 28 degrees, and a BO
The removal rate was D.

同様に褐色廃液透視度0度、COD175ppmに媒体
を与えた結果は透視度28度、C0D23.4 ppm
でCOD除去率86.6L01)であった。
Similarly, when medium was applied to brown waste liquid with transparency of 0 degrees and COD of 175 ppm, the results were as follows: transparency of 28 degrees and COD of 23.4 ppm.
The COD removal rate was 86.6L01).

2)直径20syttの球形に成型焼成した媒体を21
容量シリンダー中に1.2i!’充填し、水産加工廃液
2tに適用した結果は、約30分後より分離現象をみた
2) A medium formed and fired into a spherical shape with a diameter of 20sytt is
1.2i in the capacity cylinder! As a result of filling the product and applying it to 2 tons of seafood processing waste liquid, a separation phenomenon was observed after about 30 minutes.

この廃液は血液及び脂肪酸を含む悪臭外しいもので透視
度0度である。
This waste liquid contains blood and fatty acids, has a foul odor, and has a visibility of 0 degrees.

通常廃液処理工程に於ける血液分除去は仲々困難である
がこの媒体を与えて3時間後には分離沈澱は終了し、脂
肪酸はケン化し、血液と共に沈澱した。
Although it is usually difficult to remove blood in the waste liquid treatment process, separation and precipitation were completed 3 hours after this medium was applied, and the fatty acids were saponified and precipitated together with the blood.

この時の廃液中のBODは6320 ppm透視度0で
処理後はBOD2270 ppm、透視度25度、BO
D除去率は64チであった。
The BOD in the waste liquid at this time was 6320 ppm with a transparency of 0, and after treatment the BOD was 2270 ppm, the transparency was 25 degrees, and the BO
The D removal rate was 64.

また悪臭は半減した。Also, the bad odor was reduced by half.

3)直径40111M長さ45Mの円筒形に成型焼成し
た媒体を306容量のプラスチック容量に121に投入
し、給食センター廃液20/に適用した結果は、約20
分後より分離現象をみた。
3) A medium molded and fired into a cylindrical shape with a diameter of 40111M and a length of 45M was put into a plastic capacity of 306 to 121, and the result of applying it to the waste liquid of the school lunch center was approximately 20
A separation phenomenon was observed after a few minutes.

この廃液は油脂分、野菜色素、洗剤を含む臭気のあるも
ので透視度8度であったが約30分後分離沈澱は終了し
た。
This waste liquid contained oils and fats, vegetable pigments, and detergents and had an odor and had a transparency of 8 degrees, but the separation and precipitation were completed after about 30 minutes.

野菜の色素は完全に分離し、透視度は30度になった。The vegetable pigments were completely separated and the visibility was 30 degrees.

この時の廃液のBODは257 ppm から32.
8 ppm となりBOD除去率は87.24係であ
った。
The BOD of the waste liquid at this time ranged from 257 ppm to 32.
8 ppm, and the BOD removal rate was 87.24%.

4)3)で用いたものと同じ円筒形に焼成した媒体を1
0朋〜15朋の大きさに破砕して不定形にして21容量
シリンダー中に1.8/充填し、無電極ニッケルメッキ
廃液2/に適用した結果は、20分後より反応をみせ、
1時間後に分離現象を起した。
4) The same cylindrical fired medium used in 3) was
It was crushed into 0 to 15 mm size, made into an amorphous shape, and filled into a 21-capacity cylinder at 1.8 mm, and applied to electrodeless nickel plating waste liquid.
A separation phenomenon occurred after 1 hour.

この廃液はニッケル燐酸塩を主にし、メタノールを1係
以上含んでいるが、ニッケル分を除去するために水酸化
ニッケルにした場合、燐酸塩を残し、Ca (OH)
2 による凝集法を行なうと二酸化ニッケルの凝集物
が多量にして濾過が極めて困難であった。
This waste liquid mainly contains nickel phosphate and contains more than one part of methanol, but when it is converted to nickel hydroxide to remove the nickel, phosphate remains and Ca (OH) is produced.
When the agglomeration method according to No. 2 was carried out, a large amount of nickel dioxide agglomerates was produced, making filtration extremely difficult.

然しこの媒体を与えることにより、2時間後に分離沈澱
がおこり、濾過も容易で88分は少量であった。
However, by providing this medium, a separated precipitate occurred after 2 hours, and it was easy to filter, and the amount was small after 88 minutes.

C0D35000 ppm、着色線透明色のメッキ廃液
は、凝集法ではCOD 22578 ppmで無色透明
であったが、この媒体分離法ではC0D 17800 ppmで無色透明であった。
The plating waste liquid, which had a COD of 35,000 ppm and a transparent colored line, was colorless and transparent with a COD of 22,578 ppm in the aggregation method, but was colorless and transparent with a COD of 17,800 ppm in this medium separation method.

メタノール含有のため浄化は容易ではないが、除去率は
凝集法の35.5%に対し、この媒体分離法では50係
の結果を得た。
Although it is not easy to purify because it contains methanol, the removal rate was 35.5% in the coagulation method, whereas the removal rate was 50% in this media separation method.

なお凝集法による一次処理水を中和し、活性岩吸着を行
なってもCOD値は、20580ppmでこの媒体CO
D除去には及ばなかった。
In addition, even if the primary treated water by the coagulation method is neutralized and activated rock adsorption is performed, the COD value is 20,580 ppm, and this medium CO
It did not reach the level of D removal.

5)3)で用いたものと同じ円筒形焼成媒体を301プ
ラスチツク容器に81充填し、食品加工廃液中の製餡廃
池及びクリーニング廃液にそれぞれ適用し、また豚し尿
に対しては不定形とした媒体を試験管に充填して適用し
た結果は、製餡廃液は20分、クリーニング廃液は30
分、豚し尿は5時間にて分離した。
5) The same cylindrical firing medium used in 3) was filled into 81 plastic containers of 301 and applied to the bean paste waste pond and cleaning waste liquid in the food processing waste liquid. The results of filling test tubes with the medium and applying it were as follows: 20 minutes for bean-making waste liquid and 30 minutes for cleaning waste liquid.
The pig human waste was separated in 5 hours.

なお、それぞれの廃液に促進剤を微量加えることにより
、反応を5分位でおこし、30分で分離を終了させるこ
とができだ。
By adding a small amount of promoter to each waste liquid, the reaction can be started in about 5 minutes and the separation can be completed in 30 minutes.

6)直径10朋の球形焼成媒体を100CCのビーカー
に80CC充填し、硫酸第二鉄100 ppm溶解液に
適用した結果は、褐色の硫酸第二鉄溶解液は5分後に反
応を開始し、脱硫と鉄の分離現象を起した。
6) A 100cc beaker was filled with 80cc of spherical firing medium with a diameter of 10mm, and the result was that the brown ferric sulfate solution started to react after 5 minutes, and desulfurization occurred. and the separation of iron occurred.

この反応は媒体自体のイオン性に基づくとみられるが、
分離物質は完全に水に離れ沈澱現象もおこした。
This reaction seems to be based on the ionic nature of the medium itself;
The separated substance was completely separated from water and a precipitation phenomenon occurred.

7)排気ガスの浄化能については本件合成媒体が排出ガ
スに対し触媒作用を発揮できるか、次の条件のなかで試
験をした。
7) Regarding exhaust gas purification ability, tests were conducted under the following conditions to see if the synthetic medium could exert a catalytic effect on exhaust gas.

排出ガスとしてC3H,、CO,NOxを選んだが、そ
の濃度はC3H62410ppm、 CO5,1係、N
Ox 47 ppmであった。
C3H, CO, and NOx were selected as exhaust gases, and their concentrations were C3H62410ppm, CO5, 1st part, and N
Ox content was 47 ppm.

その中でC3H6、CαCλ・ては、本件合成媒体量を
24 tttlとし、通過ガス量を、それぞれ16 t
/rnirtにて温度条件をかえながら浄化能を測定し
た。
Among them, for C3H6 and CαCλ, the amount of synthesis medium in this case is 24 tttl, and the amount of passing gas is 16 t.
The purification ability was measured while changing the temperature conditions at /rnirt.

C8H,においては、触媒入口ガス温度が350℃にお
いて浄化反応を示し、600℃前後より急激な効果反応
を示したが、700℃に至ってC3H,は100%、C
Oは65係の除去率を示した。
For C8H, a purification reaction occurred when the catalyst inlet gas temperature was 350°C, and a rapid effect reaction occurred from around 600°C, but when the temperature reached 700°C, C3H was 100%, and C
O showed a removal rate of 65.

Nox については、触媒量24vtlガス流量16
/! /m1ttと前記同様であるが、温度条件を6
80℃に一定し、空燃比のみをかえ、浄化能を測定した
For Nox, catalyst amount 24vtl gas flow rate 16
/! /m1tt is the same as above, but the temperature condition is 6.
The purification ability was measured by keeping the temperature constant at 80°C and changing only the air-fuel ratio.

空燃比15.0においては反応を示さす空燃比14.7
より反応を示し触媒入口ガス空燃比14.0において急
激な触媒反応をおこし、NOx除去率65チを示した。
At an air-fuel ratio of 15.0, a reaction occurs at an air-fuel ratio of 14.7.
At the catalyst inlet gas air-fuel ratio of 14.0, a rapid catalytic reaction occurred, and the NOx removal rate was 65 cm.

以上に対し、参照のため、入来カオリン単体および大理
石を焼成して生ずるCaOの単体は脱色性を示すが長時
間を要し凝集物も多くまた大理石、シラスは単体では脱
色性を示さなかった。
In contrast to the above, for reference, imported kaolin alone and CaO produced by calcining marble exhibit decolorizing properties, but it takes a long time and there are many aggregates, and marble and shirasu do not exhibit decolorizing properties when used alone. .

さらに儀入来カオリンと珪酸石灰を等景況合し700℃
で焼成したもの、[有])入来カオリンと大理石粉末の
等景況合物の700℃焼成物およびし)入来カオリンと
シラスと酸化鉄の5:5:1混合物を1000℃で焼成
したものの着色液による脱色効果も■は24時間後に脱
色効果を示したものの脱色率は悪く着色剤の分離はみら
れず伯)は20時間後に脱色効果を示したが、透視度4
8〜20度で着色剤の分離は僅かであった。
In addition, kaolin and silicate lime were heated to 700℃ under the same conditions.
1) A mixture of kaolin and marble powder fired at 700°C, and 2) A 5:5:1 mixture of kaolin, whitebait, and iron oxide fired at 1000°C. Regarding the decolorizing effect of the colored liquid, (■) showed a decolorizing effect after 24 hours, but the decolorizing rate was poor and no separation of the colorant was observed.
At 8 to 20 degrees, there was little separation of the colorant.

また(C)は全く反応も脱色性も示さなかった。Further, (C) showed no reaction or decolorization at all.

次に媒体の効力の持続性の検討結果は次のとおりであっ
た。
Next, the results of examining the sustainability of the medium's efficacy were as follows.

すなわち、染色廃液300ccに促進剤として硫酸アル
ミ2滴を添加し試験管に1Qccづつを30本並べてそ
の1本に媒体を液面近くまで投入し反応、脱色試験を行
ったところ、2分間で分離沈澱、脱色度85係を示した
がこの1度使用した媒体を次の試験管に投入することを
繰返し、同じ2分間づつの反応で30本全部を脱色でき
た。
That is, when 2 drops of aluminum sulfate were added as an accelerator to 300 cc of dyeing waste liquid, 30 tubes of 1 Q cc were lined up in a test tube, and a medium was poured into one of the tubes to near the liquid surface to perform a reaction and decolorization test, separation occurred in 2 minutes. Although the degree of precipitation and decolorization was 85, the once-used medium was repeatedly introduced into the next test tube, and all 30 tubes were decolorized in the same 2-minute reaction.

さらにこの媒体を取り出し加熱し付着分を焼却し再生使
用したが同様な結果かえられた。
Furthermore, this medium was taken out and heated to incinerate the adhering matter and reused, but the same result was obtained.

これに対し活性炭の場合は最初は良く吸着したが回を重
ねる度にその吸着性は衰え、13本1で完全にその効力
を失った。
On the other hand, in the case of activated carbon, it adsorbed well at first, but its adsorption properties decreased with each use, and it completely lost its effectiveness after 13 times.

以上かられかるように、この媒体は各種廃液の処理に有
意義であり、また排出ガスについても上記7)の例に示
すように、窒素酸化物、−酸化炭素等の除去に効果的で
ある。
As can be seen from the above, this medium is useful in treating various waste liquids, and is also effective in removing nitrogen oxides, carbon oxides, etc. from exhaust gases, as shown in the example 7) above.

そして原料入手も加工も容易であり、かつ前述のように
媒体内部の目詰りや表面付着による老廃現象があられれ
ても、加熱するだけで容易に再生使用できるから経済的
である。
Moreover, raw materials are easy to obtain and process, and even if the medium becomes obsolete due to clogging inside the medium or adhesion to the surface as described above, it is economical because it can be easily reused by simply heating it.

Claims (1)

【特許請求の範囲】[Claims] 1 アルミナ含量の多い粘土、炭酸カルシウム含量の多
い岩石及び二酸化けい素を主成分としそれに微量の酸化
鉄、酸化カリウム、酸化ナトリウム、酸化マグネシウム
、チタンを含む火山灰の各粉末を、はぼ等量用いて混練
し、1000℃前後の高温で焼成してなる廃液および排
出ガスの脱色浄化用合成媒体。
1 Approximately equal amounts of clay with a high alumina content, rock with a high calcium carbonate content, and volcanic ash powder containing silicon dioxide as the main component and trace amounts of iron oxide, potassium oxide, sodium oxide, magnesium oxide, and titanium are used. Synthetic medium for decolorizing and purifying waste liquid and exhaust gas, which is obtained by kneading the mixture and firing at a high temperature of around 1000°C.
JP50103465A 1975-08-28 1975-08-28 High exhaustion Expired JPS5822246B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP50103465A JPS5822246B2 (en) 1975-08-28 1975-08-28 High exhaustion

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP50103465A JPS5822246B2 (en) 1975-08-28 1975-08-28 High exhaustion

Publications (2)

Publication Number Publication Date
JPS5227077A JPS5227077A (en) 1977-03-01
JPS5822246B2 true JPS5822246B2 (en) 1983-05-07

Family

ID=14354752

Family Applications (1)

Application Number Title Priority Date Filing Date
JP50103465A Expired JPS5822246B2 (en) 1975-08-28 1975-08-28 High exhaustion

Country Status (1)

Country Link
JP (1) JPS5822246B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS60261538A (en) * 1984-06-08 1985-12-24 Kogyo Kaihatsu Kenkyusho Adsorbing and removing method of nox and manufacture of adsorbent
JP6970410B2 (en) * 2018-03-29 2021-11-24 太平洋セメント株式会社 Ammonia-containing water treatment material and its manufacturing method

Also Published As

Publication number Publication date
JPS5227077A (en) 1977-03-01

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