JPS5980389A - Agent for comprehensive disposal of ammonia-contg. liquid matter and comprehensive disposal of said liquid matter - Google Patents

Agent for comprehensive disposal of ammonia-contg. liquid matter and comprehensive disposal of said liquid matter

Info

Publication number
JPS5980389A
JPS5980389A JP7831483A JP7831483A JPS5980389A JP S5980389 A JPS5980389 A JP S5980389A JP 7831483 A JP7831483 A JP 7831483A JP 7831483 A JP7831483 A JP 7831483A JP S5980389 A JPS5980389 A JP S5980389A
Authority
JP
Japan
Prior art keywords
water
ammonia
liquid
treated
precipitate
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.)
Granted
Application number
JP7831483A
Other languages
Japanese (ja)
Other versions
JPS6156018B2 (en
Inventor
Yoshimasa Igari
猪狩 俶将
Shoichiro Yokoyama
横山 正一郎
Yoshihiro Murao
村尾 好宥
Hirosaku Mukai
向 啓作
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
KANKYO GIJUTSU KAIHATSU KK
National Institute of Advanced Industrial Science and Technology AIST
Original Assignee
KANKYO GIJUTSU KAIHATSU KK
Agency of Industrial Science and Technology
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by KANKYO GIJUTSU KAIHATSU KK, Agency of Industrial Science and Technology filed Critical KANKYO GIJUTSU KAIHATSU KK
Priority to JP7831483A priority Critical patent/JPS5980389A/en
Publication of JPS5980389A publication Critical patent/JPS5980389A/en
Publication of JPS6156018B2 publication Critical patent/JPS6156018B2/ja
Granted legal-status Critical Current

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  • Removal Of Specific Substances (AREA)
  • Water Treatment By Sorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PURPOSE:To obtain the titled agent for the comprehensive disposal of ammonia- contg. liquid matter such as waste water, by mixing the specified amount of fine powdery dolomite in the dry precipitate of water granulated slag treated with an acid, and baking said mixture at 350-900 deg.C for 15min-2hr. CONSTITUTION:After granulated slag obtd. from a steel-making furnace and finely pulverized to at least 200 mesh is dissolved in an aqueous inorganic acid solution, an aqueous alkali solution is added to the aforementioned solution to make it alkaline. The resulting precipitate is washed with water, dehydrated and dried to obtain the dry precipitate of water granulated slag treated with an acid. Said dry precipitate is mixed with fine powdery dolomite at a wt. ratio of 1:1-5:1, and the mixture is baked at 350-900 deg.C for 15min-2hr to obtain the agent for the comprehensive disposal of ammonia-contg. liquid matter. When said treating agent is to be added to waste water, its addition ratio is 5-20 times the value of CODMn in the waste water.

Description

【発明の詳細な説明】 本発明はアンモニア含有液状物より同時に一アンモニア
、 COD及び色を除去する綜合処j’j14削及O・
該処理剤を使用するアンモニア含有液状物よりアンモニ
ア、 COD及び色を同時に除去1″るアンモニア含有
液状物綜合処理方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention provides a comprehensive process for simultaneously removing ammonia, COD and color from an ammonia-containing liquid.
The present invention relates to an integrated treatment method for an ammonia-containing liquid material that uses the processing agent to simultaneously remove ammonia, COD, and color from an ammonia-containing liquid material.

従来、排水、廃液等のCODの除去あるいは巳の除去に
関しては多(の技術があり、また続々としてその開発か
なされつつある。
Conventionally, there are many technologies for removing COD or COD from waste water, waste liquid, etc., and they are being developed one after another.

一方、脱窒技術としてはたとえばアンモニアス]・リツ
ピ/グ法、生物化学的硝化・脱窒法1選択的イオン交換
法、不連続点塩素注入処理法等があり、その中アンモニ
アストリッピング法にも各種の技術か展開されている。
On the other hand, denitrification techniques include, for example, the ammonia removal/denitrification method, the biochemical nitrification/denitrification method, the selective ion exchange method, and the discontinuous point chlorine injection treatment method, among which the ammonia stripping method also Various technologies are being developed.

しかし排水、廃液あるいはその他の液状物中のアンモニ
ア、 COD及び色を同時に除去することは、従来困難
であり、未だ丁ぐれ1こしかも経済的な方法は存在しな
い。
However, it has been difficult to simultaneously remove ammonia, COD, and color from waste water, waste liquid, or other liquid materials, and there is still no simple and economical method.

本発明者らはかかる点に着目し、鋭意研究を1ねた結果
、本発明に到達したものであり、その要旨と1−るとこ
ろは上記の如く排水、廃液あるいはその他の液状物中の
アンモニア、 COD及び色を同時に除去1−ろアンモ
ニア含有液状物綜合処理剤並びに該削によるアンモニア
含有敵状物の綜合処理力法に存し、評しくは、少なくと
も21)0メツシユに微粉(ヒしTこ製鉄炉から得られ
る水砕スラグ(以下単に水砕スラグという)を無機酸水
浴液に溶解し、アルカリ水溶液をさらに添加することに
より該溶液をアルカリ性となし、析出した沈澱物をiH
i別、水洗し、ついで該水洗沈澱物を脱水乾燥して得ら
れた酸処理水砕スラグ乾燥沈澱物+4Cさらに微粉状ド
ロマイトを重量比にて1:1乃至5:1の割合にて混加
し、該混合物を350乃至9(H)℃の温度にて15分
乃至2時間焼成したアンモニア含イーj液状物綜合処理
剤に存し、さらに本発明の一要旨と1−るところは上記
焼成酸処理水砕スラグ・ドロマイト混合処理剤を、被処
理液状物中のCOI)M、 11に対し5乃至20倍量
にて該被処理液状物に添加し、該添加被処理液状物中に
空気あるいは水蒸気を、上記被処理tL状物中のCOD
Mn量対上記処理剤の添加率が上記比率内に維持される
ような量で少なくとも1時間通導し、ついで被処理液状
物中の処理剤をp別号離し、かくしてアンモニア含有液
状物よりアンモニア、 COD及び色を同時に除去1−
るアンモニア含有液状物綜合処理方法に存する。
The inventors of the present invention have focused on this point, and as a result of intensive research, they have arrived at the present invention. , COD and color can be simultaneously removed by using a comprehensive treatment agent for ammonia-containing liquid materials and a comprehensive treatment method for ammonia-containing liquid materials by said cutting, preferably at least 21)0 meshes of fine powder (HishiT). The granulated slag obtained from this iron-making furnace (hereinafter simply referred to as granulated slag) is dissolved in an inorganic acid water bath solution, the solution is made alkaline by further adding an alkaline aqueous solution, and the precipitate that has precipitated is heated by iH.
Acid-treated granulated slag dried precipitate +4C obtained by washing with water and then dehydrating and drying the washed precipitate +4C Further, fine powder dolomite is mixed in a weight ratio of 1:1 to 5:1. and an ammonia-containing liquid integrated processing agent obtained by baking the mixture at a temperature of 350 to 9 (H)°C for 15 minutes to 2 hours, and one aspect of the present invention is that the above-mentioned baking An acid-treated granulated slag/dolomite mixed treatment agent is added to the liquid to be treated in an amount of 5 to 20 times the amount of COI) M, 11 in the liquid to be treated, and air is added to the liquid to be treated. Alternatively, the COD in the to-be-treated material is
Conducting the treatment for at least 1 hour in such an amount that the addition ratio of Mn to the treatment agent is maintained within the above ratio, and then the treatment agent in the liquid to be treated is separated, thus removing ammonia from the ammonia-containing liquid. , COD and color removal at the same time 1-
The present invention relates to a method for comprehensively treating an ammonia-containing liquid material.

本発明に於て使用されろ水砕スラグは製鉄炉から得られ
るスラグを急冷したものであり、例えば高炉水砕スラグ
の組成の1例を示せば第1表の通りである。
The granulated slag used in the present invention is obtained by rapidly cooling slag obtained from a steelmaking furnace, and an example of the composition of granulated blast furnace slag is shown in Table 1.

本発明に於て水砕スラグを溶解する無機酸としては例え
ばHCt、 HNO3、J(2SO4、ICto4等が
好ましく使用され、溶解温度室温あるいは100 Cま
での加温に於て水砕スラグを溶解した無機酸水浴液に添
加1〜ろアルカリ水溶液としては例えばNaOH。
In the present invention, as the inorganic acid for dissolving the granulated slag, for example, HCt, HNO3, J(2SO4, ICto4, etc.) are preferably used. An example of the aqueous alkali solution added to the inorganic acid aqueous solution is NaOH.

KOII 、 NI+4011 、 (N112 )2
 Co等の水浴液が使用される。
KOII, NI+4011, (N112)2
A water bath solution such as Co is used.

なお、無機酸水浴液としてはIN乃至5N水浴液が好ま
しく使用され、無機酸水溶’171100 mlに対し
最高157の割合で水砕スラグを添加するのが好ましく
−8 本発明に於て使用する水砕スラグは少なくとも200メ
ツシユに微粉化したものであるか、200メツシユ以上
のものを使用すると無機酸に対するd)解性が低下し、
溶解残渣が残ってしまうので好ましくない。
As the inorganic acid water bath solution, an IN to 5N water bath solution is preferably used, and it is preferable to add granulated slag at a maximum ratio of 157 to 171,100 ml of the inorganic acid aqueous solution. The crushed slag must be pulverized to at least 200 mesh, or if more than 200 mesh is used, d) disintegration with inorganic acids will decrease;
This is not preferable because a dissolved residue remains.

焼成温度については、350℃以下及び900℃以上で
あるといずれも焼成物の比表面積が小さく、したかつて
吸着反応性が低下する。
Regarding the firing temperature, if the firing temperature is 350° C. or lower or 900° C. or higher, the specific surface area of the fired product will be small, and the adsorption reactivity will decrease.

焼成時間については、焼成温度と関係があり、焼成温度
900℃の場合は15分、350℃の場−8′2時間の
焼成時間が必要である。
The firing time is related to the firing temperature; if the firing temperature is 900°C, the firing time is 15 minutes, and if the firing temperature is 350°C, the firing time is 8'2 hours.

処理剤の添加割合については、排水中のC01)M。Regarding the addition ratio of treatment agent, C01)M in wastewater.

量に対して5乃至20倍量であり、排水中の有機物の含
有量との関係から得られたものであり、通常5乃至20
倍量であれば充分である。
It is 5 to 20 times the amount, and is obtained from the relationship with the content of organic matter in wastewater, and is usually 5 to 20 times the amount.
Double the amount is sufficient.

空気あるいは水蒸気の通導量については、アンモニアの
除去と関連し、通導量は温度とpiにより支配され、そ
の場合上記添加量すなわち5乃至20倍量が維持できる
ように適宜決定されるものである。
The amount of air or water vapor conducted is related to the removal of ammonia, and is controlled by temperature and pi, in which case it should be appropriately determined so as to maintain the above-mentioned addition amount, that is, 5 to 20 times the amount. be.

以下に実施例を示し本発明をさらに詳細に説+jJJす
る。
The present invention will be explained in more detail below with reference to Examples.

実施例 第1表に示す約230メツンユに微粉化した高炉水砕ス
ラグ1007を4N −HCt水溶液1000 rnl
、に加え、マグイ・チンクスターラーを用いて20Or
、p、m。
Example: Granulated blast furnace slag 1007 pulverized to about 230 ml as shown in Table 1 was added to a 4N-HCt aqueous solution of 1000 rnl.
, plus 20 Or
, p, m.

で攪拌して溶液を得、これに水1000 mJを添加し
、ついて4N −Na0Il水浴液を徐々に加え溶液の
pJ(を11.0とした。か(して析出した沈澱物をj
3別し、洗滌液のpHが7乃至8になるまで水洗し、該
水洗沈澱物を110℃にた約12時間乾燥して得られた
焼成前の酸処理水砕スラグ乾燥沈澱物に微粉状ドロマイ
トを1=1の重量比にて混加し、該混合物を8[10℃
の温度にて1時間焼成して焼成1ツ処理水砕スラグ・ド
ロマイト混合処理剤(ADSD)を得た。
To this, 1000 mJ of water was added, and then a 4N-Na0Il water bath solution was gradually added to bring the pJ of the solution to 11.0.
3, washed with water until the pH of the washing solution became 7 to 8, and dried the water-washed precipitate at 110°C for about 12 hours. Dolomite was mixed in a weight ratio of 1=1, and the mixture was heated to 8 [10°C
The mixture was fired at a temperature of 1 hour to obtain a fired granulated slag/dolomite mixed treatment agent (ADSD).

上記の如くにしてイ:)た処理剤いDSD丹こよる(1
)都市廃棄物埋立浸出水及び(2)活性汚泥処理糖蜜廃
水の処理は以下の辿りである。
As above, use the processing agent DSD Tankoyoru (1).
) Municipal waste landfill leachate and (2) activated sludge treated molasses wastewater are treated as follows.

(1)p■I7.70.CODMn764ppm1色度
1.244(457nm吸光度)及びアンモニア716
 ppmの都市廃棄物埋立浸出水1000m1!に対し
、上記処理剤(ADS)を該浸出水中のCODMo量に
対し10倍量添加し、約80℃にて該被処理液中に留出
液鼠が2mVmtnになる、Lうに水蒸気を1時間通導
した。
(1)p■I7.70. CODMn764ppm1 chromaticity 1.244 (457nm absorbance) and ammonia 716
ppm municipal waste landfill leachate 1000ml! To this, the above-mentioned treatment agent (ADS) was added in an amount 10 times the amount of CODMo in the leachate, and sea urchin water vapor was added to the treated liquid at about 80°C for 1 hour so that the distillate concentration was 2 mVmtn. It was communicated.

(2) pH7,53、CODMn797 pptn 
、色度1.835(457町吸光度〕及びアンモニア7
95 ppmの活性汚泥処理糖蜜廃水を上記(1)と同
一条件にて処理した。
(2) pH 7,53, CODMn797 pptn
, chromaticity 1.835 (absorbance 457) and ammonia 7
95 ppm activated sludge treated molasses wastewater was treated under the same conditions as in (1) above.

結果は第2表の通りである。The results are shown in Table 2.

第  2  表 第2表の結果より焼成酸処理水砕スラグ・ドロマイト混
合処理剤はCODの除去及び色度−の低減にすぐれ、と
くにアンモニアの除去に顕著でありlこ。
Table 2 The results shown in Table 2 show that the calcined acid treated granulated slag/dolomite mixture treatment agent is excellent in removing COD and reducing chromaticity, especially in removing ammonia.

6060

Claims (1)

【特許請求の範囲】 (り少なくとも200メツシユに微粉化1−た製鉄炉か
ら11すられる水砕スラグを2J((機酸水浴液に浴解
し、アルカリ水、答液をさら罠添加することにより該溶
液をアルカリ性となし、析出し1こ沈澱物をカ1i別、
水洗1〜、ついで該水洗沈澱物を脱水乾燥して得られた
酸処理水砕スラグ乾燥沈澱物に、さらに微粉状ドロマイ
トを重量比にて1=1乃至5:1の割合にて混加し、該
混合物を350乃至9001cの温度にて15分乃至2
時間焼成したアンモニア含有液状1勿綜合処」里斉り。 (2)少なくとも200メツ/ユに微粉化した製鉄炉か
らT44られる水砕スラグを無機1竣水浴液に浴解し、
アルカリ水浴液をさらに添加することにより該浴液をア
ルカリ性となし、析出した沈澱物をp別、水洗し、つい
で該水洗沈澱物を脱水乾燥して得られ1こ酸処理水砕ス
ラグ乾燥沈澱物に、さらに微粉状ドロマイトを重量比に
て1:1乃至5:1σ) ’、’+1合九で混加した混
合物を350乃至900℃のl、情度にて15分乃至2
時間焼成した焼成混合物を、被処理液状物中のCOD、
、□n量に対し5乃至20イr″”; tlt IIC
てfツム処理液状物に添加し、該添加被処理液状物11
JK空気あるいは水蒸気を、上記被処理液状物中のCO
1)N4 、。 量対上記添加物の添加率が上記比率内に維持されるよう
な量にて少なくとも1時間通導し、ついて被処理液状物
中の処理剤をf別号離し、かくしてアンモニア含有液状
物より、アンモニア、 C0I)及び色を同時に除去1
−るアンモニア含有液状物綜合処理方法。
[Scope of Claims] (2J) of granulated slag scraped from a steelmaking furnace, which has been pulverized to at least 200 meshes, is dissolved in a mechanical acid water bath solution, and alkaline water and solution are further added. The solution was made alkaline, and the precipitate was separated by
After washing with water 1~, the water-washed precipitate was then dehydrated and dried to obtain an acid-treated granulated slag dry precipitate, and finely powdered dolomite was further mixed in a weight ratio of 1=1 to 5:1. , the mixture was heated at a temperature of 350 to 9001C for 15 minutes to 2
Time-fired ammonia-containing liquid 1. (2) The granulated slag produced by T44 from a steelmaking furnace pulverized to at least 200 Metz/U is bath-dissolved in an inorganic 1 finished water bath solution,
The bath liquid is made alkaline by further adding an alkaline water bath liquid, and the precipitated precipitate is separated and washed with water, and then the water-washed precipitate is dehydrated and dried to obtain a dried precipitate of 1-sulfuric acid-treated granulated slag. Then, a mixture of finely powdered dolomite was added at a weight ratio of 1:1 to 5:1σ)','+1 to 9, and the mixture was heated at 350 to 900°C for 15 minutes to 2.
COD in the liquid to be treated,
, □5 to 20 ir'' for the amount of n; tlt IIC
and add it to the liquid material to be treated with
JK air or water vapor is used to remove CO in the liquid to be treated.
1) N4,. conduction for at least 1 hour in such an amount that the addition ratio of the additive to the amount is maintained within the above ratio, thereby removing the processing agent in the liquid to be treated, thus removing the ammonia-containing liquid from the ammonia-containing liquid. Simultaneously removes ammonia, C0I) and color1
- A method for comprehensively treating ammonia-containing liquids.
JP7831483A 1983-05-06 1983-05-06 Agent for comprehensive disposal of ammonia-contg. liquid matter and comprehensive disposal of said liquid matter Granted JPS5980389A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7831483A JPS5980389A (en) 1983-05-06 1983-05-06 Agent for comprehensive disposal of ammonia-contg. liquid matter and comprehensive disposal of said liquid matter

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7831483A JPS5980389A (en) 1983-05-06 1983-05-06 Agent for comprehensive disposal of ammonia-contg. liquid matter and comprehensive disposal of said liquid matter

Related Parent Applications (1)

Application Number Title Priority Date Filing Date
JP1342079A Division JPS598418B2 (en) 1979-02-09 1979-02-09 Ammonia-containing liquid material comprehensive treatment agent and the liquid material comprehensive treatment method

Publications (2)

Publication Number Publication Date
JPS5980389A true JPS5980389A (en) 1984-05-09
JPS6156018B2 JPS6156018B2 (en) 1986-12-01

Family

ID=13658474

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7831483A Granted JPS5980389A (en) 1983-05-06 1983-05-06 Agent for comprehensive disposal of ammonia-contg. liquid matter and comprehensive disposal of said liquid matter

Country Status (1)

Country Link
JP (1) JPS5980389A (en)

Also Published As

Publication number Publication date
JPS6156018B2 (en) 1986-12-01

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