JPH11216479A - Composition for collecting phosphate ion - Google Patents

Composition for collecting phosphate ion

Info

Publication number
JPH11216479A
JPH11216479A JP5877898A JP5877898A JPH11216479A JP H11216479 A JPH11216479 A JP H11216479A JP 5877898 A JP5877898 A JP 5877898A JP 5877898 A JP5877898 A JP 5877898A JP H11216479 A JPH11216479 A JP H11216479A
Authority
JP
Japan
Prior art keywords
water
composition
phosphate
granular composition
phosphate ion
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
JP5877898A
Other languages
Japanese (ja)
Inventor
Tsutomu Nakamura
務 中村
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.)
SEIBUTSU KANKYO SYSTEM KOGAKU
SEIBUTSU KANKYO SYSTEM KOGAKU KENKYUSHO KK
Original Assignee
SEIBUTSU KANKYO SYSTEM KOGAKU
SEIBUTSU KANKYO SYSTEM KOGAKU KENKYUSHO KK
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 SEIBUTSU KANKYO SYSTEM KOGAKU, SEIBUTSU KANKYO SYSTEM KOGAKU KENKYUSHO KK filed Critical SEIBUTSU KANKYO SYSTEM KOGAKU
Priority to JP5877898A priority Critical patent/JPH11216479A/en
Publication of JPH11216479A publication Critical patent/JPH11216479A/en
Pending legal-status Critical Current

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  • Removal Of Specific Substances (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a practical means for collecting and recovering phosphate ion contained in a waste water, a water of the river, the lake or the like and causing eutrophication in a form capable of reutilizing. SOLUTION: The practical means for collecting phosphate ion in the water in the form capable of reutilizing i.e., as calcium phosphate is carried out by allowing a powder of bentonite of a clay containing montmorillonite as a main clay mineral and calcium carbonate to react with a water soluble high polymer such as a polyvinyl alcohol to prepare a water resistant granular composition, charging the water resistant granular composition into a column or a net like bag and bringing it into contact with the water containing phosphate ion such as the waste water, the water of the river, the lake or the lake.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、水中のリン酸イオンを
再利用可能な形で回収する組成物に関するものであり、
環境保護、農業の分野で利用されるものである。
The present invention relates to a composition for recovering phosphate ions in water in a reusable form,
It is used in the fields of environmental protection and agriculture.

【0002】[0002]

【従来の技術】従来、鉄材を排水中に浸漬して、鉄表面
から溶出する鉄イオンと排水中のリン酸イオンを結合さ
せて難溶性のリン酸鉄塩として沈殿させる方法が提案さ
れている。この方法では、貴重な資源としてのリン酸の
回収・再利用は考えられていない。従来、排水中は勿
論、河川、湖沼に存在し、富栄養価をもたらし、水質の
悪化の主原因の一つになっているリン酸イオンを再利用
可能な形で回収する実用的方法は存在しない。
2. Description of the Related Art Conventionally, there has been proposed a method in which an iron material is immersed in wastewater, and iron ions eluted from the iron surface and phosphate ions in the wastewater are combined to precipitate as a hardly soluble iron phosphate salt. . In this method, recovery and reuse of phosphoric acid as a valuable resource is not considered. Conventionally, there is a practical method for recovering phosphate ions, which are present not only in wastewater but also in rivers and lakes, provide eutrophication and are one of the main causes of water quality deterioration, in a reusable form. do not do.

【0003】[0003]

【発明が解決しようとする課題】従来実用技術として存
在しない、排水、河川、湖沼中のリン酸イオンを再利用
可能な形で捕集、回収する方法を提供することを課題と
した。
SUMMARY OF THE INVENTION An object of the present invention is to provide a method of collecting and recovering phosphate ions in wastewater, rivers, lakes and marshes in a reusable form, which does not exist as a conventional practical technique.

【0004】[0004]

【課題を解決するための手段】前述の課題を解決するた
めの手段について鋭意研究した結果、本発明者が到達し
た手段は、モンモリロナイトを主粘土鉱物とする粘土で
あるベントナイトと炭酸カルシュウム粉末の混合物と水
溶性高分子化合物より成る、耐水性複合体の粒状組成物
を用いて、水中のリン酸イオンを捕集する方法である。
本発明について更に詳しく説明すると、ベントナイトと
炭酸カルシュウム粉末の混合物に水溶性高分子化合物の
水溶液を加えて混合した後、造粒して乾燥し耐水性の粒
状組成物を得る方法を採っても良く、また、ベントナイ
トと炭酸カルシュウム粉末の混合物に水溶性高分子化合
物の水溶液を加え混合した後、乾燥したものを砕いて、
耐水性の粒状組成物を得る方法を採用しても良い。粒状
組成物の粒径は1.0mmから5.0mm位が扱い易い
が、この範囲に限るものではない。また、予めベントナ
イトと炭酸カルシュウム粉末の水懸濁液を作っておい
て、その中へ水溶性高分子化合物の水溶液を加える方法
を採用して、反応物を造粒−乾燥、または、乾燥−粉砕
工程をとおしても、目的とする耐水性の粒状組成物が得
られる。乾燥の方法としては、通常の加熱乾燥、熱風乾
燥の他、凍結乾燥を採用することが可能である。
Means for Solving the Problems As a result of earnest studies on means for solving the above-mentioned problems, the means reached by the present inventors is a mixture of bentonite, which is a clay having montmorillonite as a main clay mineral, and calcium carbonate powder. This is a method for trapping phosphate ions in water using a granular composition of a water-resistant composite comprising a water-soluble polymer compound and a water-soluble polymer compound.
To describe the present invention in more detail, after adding and mixing an aqueous solution of a water-soluble polymer compound to a mixture of bentonite and calcium carbonate powder, a method of granulating and drying to obtain a water-resistant granular composition may be employed. Also, after adding and mixing an aqueous solution of a water-soluble polymer compound to a mixture of bentonite and calcium carbonate powder, crushing the dried product,
A method of obtaining a water-resistant granular composition may be employed. The particle size of the granular composition is easy to handle from about 1.0 mm to about 5.0 mm, but is not limited to this range. Also, a method of preparing an aqueous suspension of bentonite and calcium carbonate powder in advance and adding an aqueous solution of a water-soluble polymer compound to the suspension is used to granulate and dry or dry-pulverize the reaction product. Through the steps, the desired water-resistant granular composition can be obtained. As a drying method, freeze drying can be employed in addition to ordinary heating drying and hot air drying.

【0005】本発明による、水中のリン酸イオン捕集用
の粒状組成物中に含まれるベントナイトの割合は98.
5から55.0重量%で、残りの部分が炭酸カルシュウ
ム粉末と水溶性高分子化合物である。使用するベントナ
イトの置換性カチオンはNaイオンでもCaイオンでも
良い。ただ、ベントナイトの陽イオン交換能は、50m
g当量/100g・粘土以上であることが望ましい。炭
酸カルシュウム粉末の量は、1.0から54.0重量%
の範囲で粒状組成物に含まれるが、特に、1.0から2
5.0重量%含まれたものが取り扱い上良い。また、炭
酸カルシュウム粉末の粒径は、100メッシュのフルイ
をとおしたものが望ましいが、その範囲に限らない。バ
インダーとしての水溶性高分子化合物としては、ポリビ
ニルアルコールとそのシラノール変性物が、粒状組成物
に耐水性を付与するのに優れているものである。水溶性
高分子化合物が粒状組成物の中に含まれる割合は、0.
5から5.0重量%が良い。バインダーの含量は、粒状
組成物の膨潤度に関わる。バインダーとしての水溶性高
分子化合物としては、上述のポリビニルアルコール系以
外に、ポリアクリル酸ソーダ、アルギン酸ソーダ等のポ
リアニオン系水溶性化合物をポリビニルアルコール系化
合物に混合して用いても良い。
According to the present invention, the proportion of bentonite contained in the particulate composition for collecting phosphate ions in water is 98.
From 5 to 55.0% by weight, the balance is calcium carbonate powder and a water-soluble polymer compound. The replaceable cation of the bentonite used may be Na ion or Ca ion. However, the cation exchange capacity of bentonite is 50m
g equivalent / 100 g clay is desirable. The amount of calcium carbonate powder is 1.0 to 54.0% by weight.
Is included in the granular composition in the range of 1.0 to 2
Those containing 5.0% by weight are easy to handle. The particle size of the calcium carbonate powder is preferably through a 100-mesh sieve, but is not limited to this range. As the water-soluble polymer compound as a binder, polyvinyl alcohol and a silanol-modified product thereof are excellent in imparting water resistance to the granular composition. The ratio of the water-soluble polymer compound contained in the granular composition is 0.1%.
5 to 5.0% by weight is good. The content of the binder is related to the degree of swelling of the particulate composition. As the water-soluble polymer compound as the binder, a polyanionic water-soluble compound such as sodium polyacrylate or sodium alginate may be used as a mixture with the polyvinyl alcohol-based compound in addition to the above-mentioned polyvinyl alcohol-based compound.

【0006】[0006]

【作用】次に、本発明の作用について説明する。194
0年代のわが国の環境保護政策により、排水中のBO
D、COD値が規制され、河川、湖沼、港湾水域での水
質の汚染度は大きく進まなくなっている。しかし、河
川、湖沼に関するかぎり、窒素化合物やリン化合物によ
る富栄養価は進んでいるといえる。それをリン酸イオン
に関していうと、有効に水中から除去する実用的な方法
が無いのが現状である。また、リン酸イオンは植物に必
須のものであるが、資源としては限られており貴重なも
のである。また、リン酸イオンが自然条件下で植物に利
用されるのは、1価か2価のカチオンとの化合物であ
り、鉄やアルミニウムとの化合物は植物には利用され難
いのである。それ故、水中のリン酸イオンを回収する
際、それが再利用を目的とするならば、1価か2価のカ
チオンとの化合物と言う形をとる事が望ましい。幸い、
リン酸イオンはカルシュウムイオンと反応して容易に、
リン酸カルシュウム塩を作り、このものはアルカリ性下
では、水に難溶性である。本発明者が発明したリン酸イ
オン捕集用の粒状組成物は、その中にリン酸イオンをカ
ルシュウム塩の形で捕集する。そして、この粒状組成物
の中では、pHが常にアルカリ側に保たれているので、
捕集されたリン酸カルシュウム塩は水に溶けずに回収さ
れるのである。回収されたリン酸カルシュウム塩を含む
粒状組成物は、リン酸肥料として、また、土壌改良材と
して有効利用できるのである。
Next, the operation of the present invention will be described. 194
Due to Japan's environmental protection policy in the 0s, BO in wastewater
The D and COD values have been regulated, and the pollution degree of water quality in rivers, lakes and marshes and harbor waters has not progressed much. However, as far as rivers and lakes are concerned, it can be said that the eutrophication value of nitrogen compounds and phosphorus compounds is increasing. As far as phosphate ions are concerned, there is no practical method for effectively removing them from water. Phosphate ions are essential for plants, but are limited and valuable as resources. Further, phosphate ions are used in plants under natural conditions by compounds with monovalent or divalent cations, and compounds with iron or aluminum are hardly used by plants. Therefore, when recovering phosphate ions in water, it is desirable to take a form of a compound with a monovalent or divalent cation if it is intended for reuse. Fortunately,
Phosphate ions easily react with calcium ions,
Produces calcium phosphate salt, which is poorly soluble in water under alkaline conditions. The particulate composition for phosphate ion collection invented by the present inventors traps phosphate ions therein in the form of calcium salts. And, in this granular composition, since the pH is always kept on the alkaline side,
The captured calcium phosphate salt is recovered without dissolving in water. The granular composition containing the recovered calcium phosphate salt can be effectively used as a phosphate fertilizer and as a soil conditioner.

【0007】[0007]

【実施例】1.陽イオン交換能が66mg当量/100
gのCa−ベントナイトの20%水懸濁液を500ml
作成し、それに100メッシュのフルイをとおした炭酸
カルシュウム粉末2gを入れ良く混合した後、重合度1
700、鹸化度98mol%のポリビニルアルコールの
10%水溶液を30ml加え混合、反応させて後、反応
物をプラスチックのバットに、厚さ1cmになるように
流し込み、60℃の熱風乾燥機で乾燥した。この乾燥物
を砕き、フルイにかけて粒径2.0mmから5.0mm
の耐水性粒状組成物を約70g得た。これを組成物1と
した。 2.陽イオン交換能が66mg当量/100gのCa−
ベントナイトの20%水懸濁液を500ml作成し、そ
れに100メッシュのふるいをとおした炭酸カルシュウ
ム粉末20gを入れ良く混合した後、実施例1で使用し
たポリビニルアルコールの10%水溶液を50ml加え
混合、反応させた。後は、実施例1と同じ工程を採っ
て、耐水性粒状組成物約65gを得た。これを組成物2
とした。 3.実施例1で使用したのと同じCa−ベントナイト1
00gと矢張り実施例1で使用したのと同じ炭酸カルシ
ュウム粉末8gを1000mlのビーカーに入れ粉末同
意で混合し、それに実施例1で使用したものと同じポリ
ビニルアルコールの2%水溶液を150ml加えて良く
混合し反応させた後、凍結乾燥をした。この凍結乾燥物
を砕き、フルイにかけて粒径2.0mmから5.0mm
の耐水性粒状組成物を約75g得た。これを組成物3と
した。 4.実施例2と同じ手順でサンプルを調製する際に、炭
酸カルシュウム粉末を加えずに耐水性粒状組成物を作
り、それを組成物4とした。 5.実施例1と同じ手順でサンプルを調製する際に、バ
インダーとしてのポリビニルアルコール水溶液を加えず
粒状組成物を作り、それを組成物5とした。 6.実施例1、2、3、4、5で作成した組成物1、
2、3、4、5を1mmの目のナイロン製の網をコック
の上に敷いた50ml容ビュレットに25gずつ入れ、
その上にもナイロン製の網を入れて組成物の表面を覆っ
た。各ビュレットにpH7.0の脱塩水を30mlずつ
注ぎ込み、室温で24時間置いた後、コックを開いて水
を流し出した。この際、組成物5は、粒状状態を消失し
てしまい、その後のリン酸イオンの捕集実験には適さな
くなったので実験系から除外した。次に、水を抜いた各
ビュレットにリン酸イオン濃度が6.0ppmになるよ
うに調製したリン酸第一カリ水溶液を30mlずつ注ぎ
込み5分間静置した後、コックを調節して、5から6分
かけて、リン酸塩水溶液を滴下させて回収し、そのリン
酸イオン濃度を比色法(Deniges法)で測定し
た。繰り返し実験では、注ぎ込んだリン酸塩水溶液をビ
ュレットから滴下し回収が終わると、直ぐに新しいリン
酸第一カリの水溶液30mlをビュレットに注ぎ込み、
5分間静置した後5から6分かけて耐水性粒状組成物層
を通過した液を回収し、そのリン酸イオン濃度の測定に
供した。リン酸イオンの繰り返し捕集実験は3回行った
が、その結果を表1に示した。 表1の結果から明らかなように本発明による、水中のリ
ン酸イオン捕集用粒状組成物は水中のリン酸イオンを効
率良く捕集回収出来ることが分かった。 7.各粒状組成物25gをそれぞれ200ml容ビーカ
ーに入れ、実施例5で用いたリン酸第一カリの水溶液を
90ml加え、スターラーで1時間かき混ぜたのち、各
区ビーカーの上澄液を採取してそのリン酸イオン濃度を
測定した結果、組成物1、2、3、4すべての試験区
で、リン酸イオン濃度は0.1ppmであった。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Cation exchange capacity is 66mg equivalent / 100
g of a 20% aqueous suspension of Ca-bentonite in 500 ml
Then, 2 g of calcium carbonate powder passed through a 100-mesh sieve was added and mixed well.
After adding and mixing and reacting 30 ml of a 10% aqueous solution of polyvinyl alcohol having a saponification degree of 700 and 98 mol%, the reaction product was poured into a plastic vat so as to have a thickness of 1 cm, and dried with a hot air drier at 60 ° C. This dried product is crushed and sieved to a particle size of 2.0 mm to 5.0 mm.
About 70 g of a water-resistant granular composition was obtained. This was designated as composition 1. 2. A cation exchange capacity of 66 mg equivalent / 100 g of Ca-
500 ml of a 20% aqueous suspension of bentonite was prepared, 20 g of calcium carbonate powder passed through a 100-mesh sieve was added and mixed well. Then, 50 ml of a 10% aqueous solution of polyvinyl alcohol used in Example 1 was added, mixed and reacted. I let it. Thereafter, the same steps as in Example 1 were performed to obtain about 65 g of a water-resistant granular composition. This is used as composition 2
And 3. The same Ca-bentonite 1 used in Example 1
00 g and arrowheads 8 g of the same calcium carbonate powder as used in Example 1 was placed in a 1000 ml beaker and mixed with powder consent, and 150 ml of the same 2% aqueous solution of polyvinyl alcohol as used in Example 1 was added. After mixing and reacting, the mixture was freeze-dried. This lyophilized product is crushed and sieved to a particle size of 2.0 mm to 5.0 mm.
About 75 g of a water-resistant granular composition was obtained. This was designated as composition 3. 4. In preparing a sample in the same procedure as in Example 2, a water-resistant granular composition was prepared without adding calcium carbonate powder, and was used as Composition 4. 5. When preparing a sample in the same procedure as in Example 1, a granular composition was prepared without adding an aqueous solution of polyvinyl alcohol as a binder, and was used as Composition 5. 6. Composition 1, prepared in Examples 1, 2, 3, 4, 5
25 g each of 2, 3, 4, 5 was put into a 50 ml burette laid on a cock with a 1 mm nylon mesh,
A nylon net was also placed on the top to cover the surface of the composition. 30 ml of demineralized water having a pH of 7.0 was poured into each burette, left at room temperature for 24 hours, and then the cock was opened to drain water. At this time, the composition 5 disappeared from the experimental system because the granular state disappeared and became unsuitable for the subsequent phosphate ion collection experiment. Next, 30 ml of an aqueous solution of potassium potash phosphate prepared so that the phosphate ion concentration becomes 6.0 ppm was poured into each of the burettes from which water had been drained, and allowed to stand for 5 minutes. Over a period of time, the aqueous phosphate solution was dropped and collected, and the phosphate ion concentration was measured by a colorimetric method (Deniges method). In the repetitive experiment, the poured phosphate aqueous solution was dropped from the burette, and as soon as the collection was completed, 30 ml of a new aqueous solution of potassium nitrate was poured into the burette.
After allowing to stand for 5 minutes, the liquid that passed through the water-resistant granular composition layer over 5 to 6 minutes was collected and used for measurement of the phosphate ion concentration. The experiment for repeatedly collecting phosphate ions was performed three times, and the results are shown in Table 1. As is clear from the results in Table 1, it was found that the granular composition for collecting phosphate ions in water according to the present invention can efficiently collect and collect phosphate ions in water. 7. 25 g of each granular composition was placed in a 200 ml beaker, and 90 ml of the aqueous solution of potassium potassium phosphate used in Example 5 was added thereto, and the mixture was stirred for 1 hour with a stirrer. As a result of measuring the acid ion concentration, the phosphate ion concentration was 0.1 ppm in all the test sections of compositions 1, 2, 3, and 4.

【0008】[0008]

【発明の効果】実施例で示したように、本発明は水中の
リン酸イオンを再利用可能な、リン酸カルシュウム塩と
いう形で捕集する耐水性粒状組成物を提供することが出
来た。この耐水性粒状組成物を充填したカラムに、リン
酸イオンを含む排水を流すことで、排水中のリン酸イオ
ンを捕集することができる。また、この耐水性粒状組成
物を網の袋に入れて河川に設置することで、河川に含ま
れるリン酸イオンが捕集出来る。また、網の袋を船の後
ろに吊るして、湖沼を巡ることにより、湖沼の水に含ま
れるリン酸イオンが捕集回収可能なことが実施例の結果
から分かった。
As shown in the examples, the present invention was able to provide a water-resistant granular composition capable of reusing phosphate ions in water and collecting calcium phosphate salts. By flowing wastewater containing phosphate ions through a column filled with the water-resistant granular composition, phosphate ions in the wastewater can be collected. In addition, by placing this water-resistant granular composition in a net bag in a river, phosphate ions contained in the river can be collected. In addition, it was found from the results of the examples that phosphate ions contained in the water of the lake can be collected and recovered by hanging the net bag behind the boat and going around the lake.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】モンモリロナイトを主粘土鉱物とする粘土
であるベントナイトと粉末の炭酸カルシュウムの混合物
に、水溶性高分子化合物の水溶液を加え、造粒しまたは
造粒せずに乾燥し、耐水性にした後、砕きまたは砕かず
に粒状にした、水中のリン酸イオン捕集用組成物。
An aqueous solution of a water-soluble polymer compound is added to a mixture of bentonite, which is a clay having montmorillonite as a main clay mineral, and powdered calcium carbonate, and granulated or dried without granulation to obtain a water-resistant material. A composition for collecting phosphate ions in water, which is crushed or granulated without crushing.
JP5877898A 1998-02-02 1998-02-02 Composition for collecting phosphate ion Pending JPH11216479A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5877898A JPH11216479A (en) 1998-02-02 1998-02-02 Composition for collecting phosphate ion

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5877898A JPH11216479A (en) 1998-02-02 1998-02-02 Composition for collecting phosphate ion

Publications (1)

Publication Number Publication Date
JPH11216479A true JPH11216479A (en) 1999-08-10

Family

ID=13094028

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5877898A Pending JPH11216479A (en) 1998-02-02 1998-02-02 Composition for collecting phosphate ion

Country Status (1)

Country Link
JP (1) JPH11216479A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2000048947A1 (en) * 1999-02-19 2000-08-24 Japan Science And Technology Corporation Method of removing phosphoric acid contained in wastewater
CN103881424A (en) * 2014-03-31 2014-06-25 华东交通大学 Method for preparing intercalated montmorillonite composite inorganic matter from nano calcium carbonate
CN106186119A (en) * 2016-08-29 2016-12-07 桂林新艺制冷设备有限责任公司 A kind of compound treating agent for water treatment
CZ308211B6 (en) * 2011-11-08 2020-03-04 Vysoká Škola Báňská Technická - Univerzita Ostrava Method of removing phosphates from household waste water

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2000048947A1 (en) * 1999-02-19 2000-08-24 Japan Science And Technology Corporation Method of removing phosphoric acid contained in wastewater
US6716357B1 (en) 1999-02-19 2004-04-06 Japan Science And Technology Corporation Method of removing phosphoric acid containting wastewater
CZ308211B6 (en) * 2011-11-08 2020-03-04 Vysoká Škola Báňská Technická - Univerzita Ostrava Method of removing phosphates from household waste water
CN103881424A (en) * 2014-03-31 2014-06-25 华东交通大学 Method for preparing intercalated montmorillonite composite inorganic matter from nano calcium carbonate
CN106186119A (en) * 2016-08-29 2016-12-07 桂林新艺制冷设备有限责任公司 A kind of compound treating agent for water treatment

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