JPS61278348A - Treatment of adsorbent - Google Patents

Treatment of adsorbent

Info

Publication number
JPS61278348A
JPS61278348A JP11971985A JP11971985A JPS61278348A JP S61278348 A JPS61278348 A JP S61278348A JP 11971985 A JP11971985 A JP 11971985A JP 11971985 A JP11971985 A JP 11971985A JP S61278348 A JPS61278348 A JP S61278348A
Authority
JP
Japan
Prior art keywords
adsorbent
aluminum
clay
nitrogen
phosphorus
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
Application number
JP11971985A
Other languages
Japanese (ja)
Inventor
Kazutaka Mori
一剛 森
Shigeo Yokoyama
横山 成男
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries Ltd
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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP11971985A priority Critical patent/JPS61278348A/en
Publication of JPS61278348A publication Critical patent/JPS61278348A/en
Pending legal-status Critical Current

Links

Landscapes

  • Water Treatment By Sorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PURPOSE:To spread the titled adsorbent in which the eutrophicating ingredients such as nitrogen and phosphorus present in the excrement waste water is adsorbed onto the farmland, etc. and to utilize said adsorbent as the fertilizer ingredients of the plant by contacting said adsorbent composed of a specified part by weight of zeorite and the rest of clay which has been subjected to an aluminum treatment with the excrement waste water, etc. CONSTITUTION:The adsorbent composed of 10-90pts.wt. high nitrogen- adsorptive zeolite and the rest of clay whose phosphorus adsorbability is increased by being subjected to the aluminum treatment is contacted with the excrement waste water, domestic waste water, etc. to adsorb nitrogen and phosphorus. The aluminum treatment is the operation of allowing the fine precipitate of aluminum hydroxide to adhere onto the surface of the clay by adjusting pH of the clay-suspended solution in which aluminum-containing salts are dissolved. The treatment of the used adsorbent results in unnecessaries by spreading the desired adsorbent in which nitrogen and phosphorus are adsorbed onto the farmland, etc. as the fertilizer.

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は、吸着剤処理方法に関し、特に肥料成分として
利用する吸着剤の処理方法に関する。
DETAILED DESCRIPTION OF THE INVENTION (Industrial Application Field) The present invention relates to a method for treating an adsorbent, and particularly to a method for treating an adsorbent used as a fertilizer component.

(従来の技術) 現在、国内における河川、湖、内海の水質は悪化してい
る。そのうち陸水および海水の富栄養化にともなう諸問
題は、単に赤潮や藻の異常発生による魚貝類に対する打
撃溪とどまらず、上水道源をもおびやかすようになって
いる。この富栄養化の原因は水に溶解したアンモニア性
窒素及びリン酸塩によるものとされている。
(Prior Art) Currently, the water quality of rivers, lakes, and inland seas in Japan is deteriorating. The problems associated with the eutrophication of land and seawater are not only damaging fish and shellfish due to red tide and abnormal growth of algae, but are also threatening water supply sources. The cause of this eutrophication is said to be ammonia nitrogen and phosphate dissolved in water.

また、富栄養化によって異常発生した藻類は死滅して湖
底や河床に沈積され、腐敗した場合には表流水中の溶存
酸素を消費し、さらにBODを付加することとなシ、富
栄養源を除去しない限シ、−これらの悪循環を断ち切る
ことはできないと考えられる。
In addition, algae that have grown abnormally due to eutrophication die and are deposited on the lake or riverbed, and when they rot, they consume dissolved oxygen in the surface water, add BOD, and become a source of eutrophic nutrients. Unless they are removed, it seems impossible to break this vicious cycle.

なお、リン、窒素の富栄養化の限界濃度はリンが[lL
o 2 ppm窒素が12 ppmとされている。
The critical concentration for eutrophication of phosphorus and nitrogen is [lL]
o 2 ppm nitrogen is supposed to be 12 ppm.

また、リン、窒素の同時存在は藻類の増殖に強く作用す
るとされている。
Furthermore, the simultaneous presence of phosphorus and nitrogen is said to have a strong effect on the growth of algae.

リン、窒素の発生源として大きいものはし尿や生活排水
および農地、山林からの流出塩である。また、畜産の盛
んな地方ではこれが大きな汚染源となっている場合があ
る。
The major sources of phosphorus and nitrogen are human waste, domestic wastewater, and salt runoff from farmland and forests. In addition, in areas where livestock farming is popular, this can become a major source of pollution.

リン、窒素の発生源のうち、し尿や生活排水については
、洗剤の無リン化というような代替品の使用、あるいは
下水道及び下水処理場の完備というような設備的改良に
よシ、徐々にその排出量が減少しているのが現状でおる
Of the sources of phosphorus and nitrogen, human waste and domestic wastewater can be gradually eliminated through the use of substitutes such as phosphorus-free detergents and through equipment improvements such as the installation of sewers and sewage treatment plants. The current situation is that emissions are decreasing.

しかし、農地山林からの流出塩、つtb多くは農地に散
布した^耕用肥料が雨水等により流出し、河川、湖等へ
流入することに関しては何ら処置なされていないのが現
状である。
However, the current situation is that nothing is being done to prevent salt runoff from agricultural land, mountains, and forests, and in many cases, fertilizers applied to farmland that run off with rainwater and flow into rivers, lakes, etc.

また、小規模畜産場からのし尿排水ちるいは小口家庭排
水については何ら処理されずに排出されているのが現状
である。
Furthermore, the current situation is that human waste wastewater from small-scale livestock farms and small-scale domestic wastewater are discharged without any treatment.

(発明が解決しようとする問題点) 本発明は、このような社会情勢を考慮し、鋭意研究を行
った結果、リン、窒素成分の流出が少なく、かつ、肥料
成分として利用できる排水処理吸着剤の処理方法を提案
するものである。
(Problems to be Solved by the Invention) The present invention has been developed as a result of extensive research in consideration of the social situation described above, and has been developed to create a wastewater treatment adsorbent that causes less phosphorus and nitrogen component runoff and can be used as a fertilizer component. This paper proposes a processing method for

(問題点を解決するための手段) 本発明は、ゼオライト10〜90重量部と、残部がアル
ミニウム処理を行った粘土からなる吸着剤にし尿排水あ
るいは家庭排水などの各種排水を接触させ、排水中に含
まれる窒素、リンの富栄養化成分を吸着した該吸着剤を
畑地等に散布し、植物の肥料成分として利用することを
特徴とする吸着剤の処理方法に関する。
(Means for Solving the Problems) The present invention involves bringing 10 to 90 parts by weight of zeolite into contact with various types of wastewater, such as night soil wastewater or domestic wastewater, using an adsorbent consisting of clay treated with aluminum, and The present invention relates to a method for treating an adsorbent, which is characterized in that the adsorbent adsorbing eutrophic components such as nitrogen and phosphorus contained in the soil is sprayed onto fields, etc., and used as a fertilizer component for plants.

本発明ではリン吸着性能の高いアルミニウム処理を行っ
た粘土と窒素吸着性能の高いゼオライトを家畜のし尿排
水あるいは家庭排水などの窒素あるいはリンなどを含む
排水と接触させて、吸着させる。
In the present invention, aluminum-treated clay with high phosphorus adsorption performance and zeolite with high nitrogen adsorption performance are brought into contact with wastewater containing nitrogen or phosphorus, such as livestock human waste wastewater or domestic wastewater, to adsorb it.

吸着後の上記粘土、あるいはゼオライトなどは畑地に散
布し、植物に必要な肥料成分として利用する。
After adsorption, the above-mentioned clay or zeolite is sprayed on fields and used as a fertilizer component necessary for plants.

ておシ、これを吸着するためにはプラスイオンあるいは
マイナスイオンの吸着剤が必要である。
In order to adsorb this, a positive or negative ion adsorbent is required.

ゼオライトは天然に存在するシリカ・アルミナを主成分
とするアルミノシリケートであシ、一般に陽イオン交換
容量が高い。数多くの種類が知られているが、本邦では
モルデン沸石あるいは斜ブチロール沸石が一般的である
Zeolite is an aluminosilicate mainly composed of naturally occurring silica and alumina, and generally has a high cation exchange capacity. Although many types are known, mordenite or oblique butyrolite is common in Japan.

粘土は天然に存在しており、通常、弱い陽イオン吸着性
あるいは弱い陰イオン吸着性を有しているが、吸着剤と
して使用できるほど容量は大きくない。そこで本発明で
は、アルミニウム処理を行ない、表面をプラスにチャー
ジさせ、陰イオン吸着性を増大させる。
Clays are naturally occurring and usually have weak cation or anion adsorption properties, but their capacity is not large enough to be used as an adsorbent. Therefore, in the present invention, aluminum treatment is performed to positively charge the surface and increase anion adsorption.

アルミニウム処理とは粘土を懸濁させた液中に塩化アル
ミニウムのようなアルミニウム含有塩を溶解し、pHを
調整して水酸化アルミニウムの微細沈殿を該粒子表面に
付着させるものである。例えば、AtC4t Al1(
S 04 )s e At(NO3)3などのM化合物
を1〜10wt%の割合で水に溶解して水溶液とし、こ
の水溶液をp)(6〜8程度に調整する( pH調整剤
としては、塩酸。
Aluminum treatment involves dissolving an aluminum-containing salt such as aluminum chloride in a suspension of clay, adjusting the pH, and depositing fine precipitates of aluminum hydroxide on the surface of the particles. For example, AtC4tAl1(
S04) M compounds such as At(NO3)3 are dissolved in water at a ratio of 1 to 10 wt% to form an aqueous solution, and this aqueous solution is adjusted to p)(about 6 to 8. As a pH adjuster, hydrochloric acid.

硫酸、硝酸などが、またアンモニア水、′力性ソーダな
どが使用できる)。この水溶液に水500重量部に対し
10〜100重量部の粘土を分散し、5〜60分間攪拌
して均一なスラリーとした後、酸又はアルカリを加えて
中性化しア°゛ルミニウム水酸化物を沈殿させ、粘土表
面に付着させる。その後、水洗し、乾燥すると止により
At処理が行なわれる。
(Sulfuric acid, nitric acid, etc. can also be used, as well as ammonia water, acidic soda, etc.) Disperse 10 to 100 parts by weight of clay to 500 parts by weight of water in this aqueous solution, stir for 5 to 60 minutes to form a uniform slurry, and then neutralize by adding acid or alkali to produce aluminum hydroxide. precipitates and adheres to the clay surface. Thereafter, after washing with water and drying, At treatment is performed.

上記のように調製した吸着剤を排水と接触させ、リンあ
るいは窒素を吸着させる。
The adsorbent prepared as described above is brought into contact with wastewater to adsorb phosphorus or nitrogen.

吸着剤使用後は畑地等に散布し、リン、窒素を含む肥料
として使用する。これにより、使用後の吸着剤の処理の
心配は不要となる。
After using the adsorbent, it is sprayed on fields and used as a fertilizer containing phosphorus and nitrogen. This eliminates the need to worry about disposing of the adsorbent after use.

更に本吸着剤は畑地においては土壌改良剤として作用す
ることが期待さ、れる。
Furthermore, this adsorbent is expected to act as a soil conditioner in fields.

各地の土壌状況は様々であシ、火山灰質土壌、砂質土壌
あるいは花崗石に由来するためカオリン鉱物に富んでい
る場合には土壌によるリン、窒素成分の保持作用は小さ
いので、土壌改良剤としてゼオライトなどを使用してい
る。
The soil conditions vary from place to place, and if the soil is rich in kaolin minerals, such as volcanic ash soil, sandy soil, or granite, the retention effect of the soil on phosphorus and nitrogen components will be small, so soil conditioners may be used. Zeolite is used as a material.

本発明は吸着剤を使用することによυ、排水処理をする
と同時に、使用済吸着剤を肥料として使用する有用な排
水処理方法でおる。
The present invention is a useful wastewater treatment method that uses an adsorbent to treat wastewater and at the same time uses the used adsorbent as fertilizer.

以下、本発明を実施例に従って説明する。Hereinafter, the present invention will be explained according to examples.

(実施例) 実施例1゜ 山形県板谷産のゼオライト及びアルミニウム処理を行っ
た愛知糸量のカオリナイト質粘土を吸着剤として使用し
た。
(Example) Example 1 Zeolite produced in Itaya, Yamagata Prefecture and kaolinite clay of Aichi yarn amount treated with aluminum were used as an adsorbent.

ゼオライトは&36瓢以下に粉砕したものを使用した。The zeolite used was pulverized to less than &36 kg.

カオリナイト質粘土のアルミニウム処理は粘土100重
量部を、水500重量部に10重量部の塩化アルミニウ
ムを溶解した水溶液に分散し、24時間攪拌した後3規
定の水酸化す) IJクムを添加してpHを5とした後
、洗浄デ過を行ない、乾燥することによシ実施した。
For aluminum treatment of kaolinitic clay, 100 parts by weight of the clay was dispersed in an aqueous solution of 10 parts by weight of aluminum chloride dissolved in 500 parts by weight of water, stirred for 24 hours, and then 3N hydroxide was added. After adjusting the pH to 5, the solution was washed, filtered, and dried.

排水模擬液としてリン酸及びアンモニア水を加え、po
  a度1000 ppI” F N’H4濃度100
0番 ppmの水□溶液を調製した。
Add phosphoric acid and ammonia water as a drainage simulating liquid, and
a degree 1000 ppI” F N'H4 concentration 100
A No. 0 ppm water solution was prepared.

吸着試験は第1図に示す吸着試験装置によシ試験を実施
した。第1図において、1は吸着塔であり、2及び3は
それぞれの吸着剤ペッド、4は排水模擬液供給装置、5
は液受けである。
The adsorption test was carried out using the adsorption test apparatus shown in FIG. In FIG. 1, 1 is an adsorption tower, 2 and 3 are respective adsorbent peds, 4 is a wastewater simulating liquid supply device, and 5 is an adsorption tower.
is a liquid receiver.

ゼオライト1kg、アルミニウム処理を行った粘土1k
gを、それぞれ吸着剤ペッド2,3に充填し、吸着試験
を行った。模擬液をS、 を流過させた時点の流出液の
濃度はPOニー 10 ppm 、 NHjS ppm
であシ、吸着剤による吸着が認められ、本吸着剤による
処理方法が有用であることが証明された。
1 kg of zeolite, 1 kg of aluminum-treated clay
g was filled into adsorbent peds 2 and 3, respectively, and an adsorption test was conducted. The concentration of the effluent at the time when the simulated liquid was passed through S was 10 ppm for POney, and 10 ppm for NHjS.
However, adsorption by the adsorbent was observed, proving that the treatment method using this adsorbent is useful.

次に、連続的に模擬液を供給し、破過した時点の吸着剤
の吸着容量を求めると、ゼオライトがゼオライト全量に
対し2.5%の凧、アルミニウム処理を行った粘土が該
粘土の全量に対しMCはほとんど認められなかった。
Next, by continuously supplying the simulated liquid and determining the adsorption capacity of the adsorbent at the time of breakthrough, it was found that zeolite was 2.5% of the total amount of zeolite, and aluminum-treated clay was 2.5% of the total amount of zeolite. In contrast, MC was hardly recognized.

実施例2 福島県天栄産のゼオライト及びアルミニウム処理を行っ
た広島児童のカオリナイト質粘土を吸着剤として使用し
た。ゼオライトは五56−以下に粉砕したものを使用し
た。
Example 2 Zeolite from Tenei, Fukushima Prefecture and kaolinitic clay from Hiroshima, which was treated with aluminum, were used as adsorbents. The zeolite used was pulverized to 556 mm or less.

カオリナイト質粘土のアルミニウム処理は粘土100重
量部を水500重量部に20重量部の硫酸アルミニウム
を溶解した水溶液に分散し24時間攪拌した後3規定の
水酸化ナトリウムを添加してpHを5とした後、洗浄3
過を行ない乾燥することにより実施した。
Aluminum treatment of kaolinitic clay involves dispersing 100 parts by weight of clay in an aqueous solution of 20 parts by weight of aluminum sulfate in 500 parts by weight of water, stirring for 24 hours, and then adjusting the pH to 5 by adding 3N sodium hydroxide. After that, wash 3
This was carried out by filtering and drying.

排水模擬液としてリン酸及びアンモニア水を加えPoニ
ー濃度500 ppm 、 NH4濃度500 ppm
の水溶液を調製した。
Phosphoric acid and aqueous ammonia were added as a drainage simulating liquid to give a Pony concentration of 500 ppm and an NH4 concentration of 500 ppm.
An aqueous solution was prepared.

吸着試験は第1図に示す吸着試験装置により実施した。The adsorption test was carried out using the adsorption test apparatus shown in FIG.

ゼオライト1kg、アルミニウム処理を行つ九粘土1 
kgをそれぞれ吸着剤ペッド2,3の位置に充填し、吸
着試験を行った。
1 kg of zeolite, 9 clays with aluminum treatment 1
kg was filled into the positions of adsorbent peds 2 and 3, respectively, and an adsorption test was conducted.

第2図に吸着試験結果を示す。横軸は処理液量であり、
縦軸は流出液中のpo4. NH4濃度である。本試験
の場合po4”−では40tXNI(4+ではSOtの
水量に対して、吸着によシかな′り濃度低下をさせるこ
とが可能であることがわかった。
Figure 2 shows the adsorption test results. The horizontal axis is the amount of liquid processed;
The vertical axis is po4 in the effluent. This is the NH4 concentration. In this test, it was found that it was possible to reduce the concentration by adsorption compared to the water amount of 40tXNI (4+) in the case of po4"- and SOt.

また、吸着剤の吸着容量が破過した後、つま、シ最初か
ら100を処理した後(すなわち、通過液中の濃度が原
液の濃度である5 00 ppmになったとき)の吸着
容量はゼオライトがMC2,7%、アルミニウム処理を
行った粘土がpo4”−2,0%であった。またゼオラ
イトにはpoニー 、アルミニウム処理を行った粘土に
はNH4はほとんど認められなかった。
In addition, after the adsorption capacity of the adsorbent has broken through, the adsorption capacity after processing 100% from the beginning (i.e., when the concentration in the passing liquid reaches 500 ppm, which is the concentration of the stock solution), is the adsorption capacity of the zeolite. MC was 2.7%, and po4''-2.0% was found in the aluminum-treated clay.Also, almost no pony was observed in the zeolite, and almost no NH4 was observed in the aluminum-treated clay.

吸着容量は各吸着剤によシ一定であるので、排水中のp
oニー、 iの存在量の割合に合わせ、吸着剤の量を本
発明の範囲であるゼオライト10〜90重量部、アルミ
ニウム処理粘土残部の範囲で変えて吸着塔に充填すれば
よいことがわかる。
Since the adsorption capacity is constant for each adsorbent, the p
It can be seen that the amount of adsorbent may be changed in the range of 10 to 90 parts by weight of zeolite, which is the range of the present invention, and the remainder of aluminum-treated clay, depending on the ratio of the amounts of 1 and 1 present in the adsorption tower.

本吸着剤は吸着したi 、 poニーは水などの供給に
よシ離脱することが可能であシ、畑地などに散布すれば
肥料成分として働く。また、本吸着剤に含まれるゼオラ
イトは、従来、農業用土壌改良剤として使用されておシ
、土壌に散布した場合、長年月にわたって土壌改良作用
を示力従って、本発明の使用済吸着剤(4、poニーを
吸着したもの)を畑地などへ散布することは有用であシ
、処理地の心配は不用である。
The adsorbent can be released by supplying water, etc., and if it is sprayed on fields, it will work as a fertilizer component. In addition, the zeolite contained in the present adsorbent has been used as an agricultural soil conditioner, and when sprayed on soil, it exhibits a soil improving effect for many years. 4. It is useful to spray pony adsorbed pony on fields, etc., and there is no need to worry about the treated area.

【図面の簡単な説明】[Brief explanation of drawings]

第1図は本発明を行うにあたシ使用した試験装置の概略
を示す図である。 第2図は吸着剤による吸着試験結果を示す図である。 復代理人  内 1)  明 復代理人  萩 原 亮 − 復代理人  安 西 篤 夫 第1図
FIG. 1 is a diagram schematically showing a test apparatus used in carrying out the present invention. FIG. 2 is a diagram showing the results of an adsorption test using an adsorbent. Sub-Agents 1) Meifuku Agent Ryo Hagiwara - Sub-Agent Atsuo Anzai Figure 1

Claims (1)

【特許請求の範囲】[Claims] ゼオライト10〜90重量部と、残部がアルミニウム処
理を行つた粘土からなる吸着剤にし尿排水あるいは家庭
排水などの各種排水を接触させ、排水中に含まれる窒素
、リンの富栄養化成分を吸着した該吸着剤を畑地等に散
布し、植物の肥料成分として利用することを特徴とする
吸着剤の処理方法。
An adsorbent consisting of 10 to 90 parts by weight of zeolite and the rest of the clay treated with aluminum is brought into contact with various types of wastewater such as night soil wastewater or domestic wastewater, and adsorbs eutrophic components such as nitrogen and phosphorus contained in the wastewater. A method for treating an adsorbent, which comprises spraying the adsorbent on a field or the like and using it as a fertilizer component for plants.
JP11971985A 1985-06-04 1985-06-04 Treatment of adsorbent Pending JPS61278348A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11971985A JPS61278348A (en) 1985-06-04 1985-06-04 Treatment of adsorbent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11971985A JPS61278348A (en) 1985-06-04 1985-06-04 Treatment of adsorbent

Publications (1)

Publication Number Publication Date
JPS61278348A true JPS61278348A (en) 1986-12-09

Family

ID=14768420

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11971985A Pending JPS61278348A (en) 1985-06-04 1985-06-04 Treatment of adsorbent

Country Status (1)

Country Link
JP (1) JPS61278348A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6418490A (en) * 1987-07-11 1989-01-23 Yoshiya Yoshino Method for removing eutrophied salts from water using water-granulated slag and zeolite

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6418490A (en) * 1987-07-11 1989-01-23 Yoshiya Yoshino Method for removing eutrophied salts from water using water-granulated slag and zeolite

Similar Documents

Publication Publication Date Title
Huang et al. Simultaneous removal of nutrients from simulated swine wastewater by adsorption of modified zeolite combined with struvite crystallization
Kabdaşlı et al. Nutrient recovery by struvite precipitation, ion exchange and adsorption from source-separated human urine–a review
JPS62500009A (en) Method and apparatus for removing suspended substances, biological nutrients and dissolved metal compounds from sewage contaminated with organic and/or inorganic substances
KR100848605B1 (en) Chemical reagent for the purpose of simultaneous treatment of n, p and microalgae for prevention eutrophication of water bodies
US3872002A (en) Process for extracting phosphate from solutions
Shen et al. Abating the effects of calcium on struvite precipitation in liquid dairy manure
CN103071461A (en) Preparation of xanthated loess adsorbent and application of xanthated loess adsorbent to waste water treatment
CN113058546A (en) Lanthanum-modified kaolin phosphorus removal agent and preparation method and application thereof
Bustos et al. Industrial symbiosis between the winery and environmental industry through the utilization of grape Marc for water desalination containing copper (II)
CN114455665A (en) Sewage dephosphorization agent and preparation method thereof
KR100342171B1 (en) Composition of chemicals for simultaneous removing nitrogen and phosphorus in wastewater and method for treating wastewater using the same
JPS61278348A (en) Treatment of adsorbent
CN110694585A (en) Preparation method of zirconium modified red mud phosphorus removal adsorbent
JPS61266382A (en) Manufacture of agricultural fertilizer
CN111607402B (en) Method for preparing soil conditioner by using high ammonia nitrogen wastewater and application
JPH10277541A (en) Zeolite type water purifying agent
JP2015508331A (en) Ammonia nitrogen removal from organic wastewater
CN108341475B (en) Method for preparing titanium polysilicate flocculant by using cold-rolled titanium plate pickling waste liquid and application
JPS61281093A (en) Adsorbent treatment
CN113083216A (en) Two-dimensional nickel-based composite metal oxide adsorbent, preparation method and application for removing phosphate radical
CN115321618A (en) Composite environment-friendly phosphorus and fluorine removal agent and preparation method and application thereof
CN112844304A (en) Sodium pyrophosphate modified water purification sludge/zeolite composite adsorbent and preparation method and application thereof
CN114132977B (en) Natural water body purifying agent and preparation method and application thereof
JPS5918365B2 (en) Red tide treatment agent and its manufacturing method
CN108439524A (en) One kind is for eutrophication water dephosphorization composite drug and preparation method thereof