JP2015171696A - Material for recovering phosphorus, production method of the material, and method for recovering phosphorus - Google Patents

Material for recovering phosphorus, production method of the material, and method for recovering phosphorus Download PDF

Info

Publication number
JP2015171696A
JP2015171696A JP2014049113A JP2014049113A JP2015171696A JP 2015171696 A JP2015171696 A JP 2015171696A JP 2014049113 A JP2014049113 A JP 2014049113A JP 2014049113 A JP2014049113 A JP 2014049113A JP 2015171696 A JP2015171696 A JP 2015171696A
Authority
JP
Japan
Prior art keywords
phosphorus
soluble silica
silica
recovery material
calcium silicate
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
JP2014049113A
Other languages
Japanese (ja)
Inventor
剛 明戸
Takeshi Meido
剛 明戸
優作 天本
Yusaku Amamoto
優作 天本
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.)
Taiheiyo Cement Corp
Original Assignee
Taiheiyo Cement Corp
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 Taiheiyo Cement Corp filed Critical Taiheiyo Cement Corp
Priority to JP2014049113A priority Critical patent/JP2015171696A/en
Publication of JP2015171696A publication Critical patent/JP2015171696A/en
Pending legal-status Critical Current

Links

Images

Landscapes

  • Water Treatment By Sorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Silicates, Zeolites, And Molecular Sieves (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a material for recovering phosphorus, which exhibits a high phosphorus recovery rate.SOLUTION: The material for recovering phosphorus is obtained by mixing lime with the silica being the easy-to-dissolve silica shown in the following item (1) and contains a single substance of an amorphous calcium silicate hydrate or a combined material which are shown in the following item (2). The item (1) is that the easy-to-dissolve silica is eluted from a mixture obtained by mixing an easy-to-dissolve silica-containing mineral, which is prepared by heating an original mineral to remove organic matter, with an alkali hydroxide aqueous solution having 1 M or higher concentration. The item (2) is that the single substance of the amorphous calcium silicate hydrate having 0.8-20 Ca/Si molar ratio or the combined material obtained by combining Ca(OH)with the amorphous calcium silicate hydrate.

Description

本発明は、リン含有水中のリンを吸着して回収するリン回収用資材、その製造方法、およびリン回収方法に関する。   The present invention relates to a phosphorus recovery material that adsorbs and recovers phosphorus in phosphorus-containing water, a manufacturing method thereof, and a phosphorus recovery method.

従来、我が国ではリンは天然資源として産出されず全てを輸入に頼っていた。しかし、近年、天然のリンは世界的に枯渇しつつあり、リンの価格が高騰してリンの確保が難しくなっている。そこで、天然のリンを補完または代替する手段の一つとして、下水処理場等で発生する排水等のリン含有水からリン回収用資材を用いてリンを回収して、りん酸質肥料にする技術が開発されてきた。   In the past, phosphorus was not produced as a natural resource in Japan, but all depended on imports. However, in recent years, natural phosphorus has been depleted worldwide, and the price of phosphorus has risen, making it difficult to secure phosphorus. Therefore, as one of the means to supplement or substitute for natural phosphorus, a technology for recovering phosphorus from phosphorus-containing water such as wastewater generated at sewage treatment plants using phosphorus recovery materials to make phosphate fertilizer Has been developed.

そして、前記リン回収用資材(下記の特許文献では、水処理材、脱リン材、およびリン回収材とも呼ばれている。)として珪酸カルシウムを主成分とする材料が知られている。例えば、特許文献1に記載の水処理剤は、CaO/SiOのモル比が1.5〜5の、非晶質珪酸カルシウム水和物を主成分とする物質を50〜700℃で加熱して製造されている。また、特許文献2に記載の汚水の脱リン材は、珪酸質原料と石灰質原料とを主成分とする水スラリーに気泡剤を添加して得られた原料を、高圧高温下で水熱反応により得られる非晶質珪酸カルシウム水和物である。さらに、特許文献3に記載の脱リン材は、非晶質珪酸カルシウム水和物を主成分とした略球状または中空パイプ状の成形物である。 And the material which has a calcium silicate as a main component is known as said phosphorus collection | recovery material (it is also called a water treatment material, a phosphorus removal material, and a phosphorus collection | recovery material in the following patent document). For example, in the water treatment agent described in Patent Document 1, a substance mainly composed of amorphous calcium silicate hydrate having a CaO / SiO 2 molar ratio of 1.5 to 5 is heated at 50 to 700 ° C. Manufactured. Moreover, the dephosphorization material of the sewage described in Patent Document 2 is obtained by hydrothermal reaction of a raw material obtained by adding a foaming agent to a water slurry mainly composed of a siliceous raw material and a calcareous raw material under high pressure and high temperature. The resulting amorphous calcium silicate hydrate. Furthermore, the dephosphorization material described in Patent Document 3 is a substantially spherical or hollow pipe-shaped molded product mainly composed of amorphous calcium silicate hydrate.

しかし、従来の珪酸カルシウムを主成分とするリン回収用資材は、リンとの反応速度が遅いため、リンを吸着して回収したリン回収用資材中のリンの含有率を高めるには、反応時間を長くする必要があった。また、リンを吸着して回収したリン回収用資材中のリンの含有率が低いため、りん酸質肥料として有効利用ができないなどの問題があった。   However, since the conventional phosphorus recovery material mainly composed of calcium silicate has a slow reaction rate with phosphorus, the reaction time is required to increase the phosphorus content in the phosphorus recovery material recovered by adsorbing phosphorus. It was necessary to lengthen. Moreover, since the phosphorus content in the phosphorus recovery material recovered by adsorbing phosphorus is low, there is a problem that it cannot be effectively used as a phosphate fertilizer.

この問題を解決するリン回収用資材として、特許文献4では、平均粒子径が150μm以下、細孔容積が0.3cm/g以上の多孔質の珪酸カルシウム水和物が提案され、特許文献5では、平均粒子径が10μm〜150μm、BET比表面積が80m/g以上、および細孔容積が0.5cm/g以上の多孔質で非晶質の珪酸カルシウム水和物が提案されている。
また、特許文献6では、Ca(OH)が2.5〜80wt%、Ca/Siのモル比が1.0〜7.0の、非晶質ケイ酸カルシウム水和物とCa(OH)の複合物からなるリン回収材が提案されている。該リン回収材は、リンを吸着する性能に優れ、かつリンを吸着した複合物は沈降性が高いため、リンの除去効果が高く、処理時間を短縮できるなどの効果を有する(段落0009)。
さらに、特許文献7では、Ca/Siのモル比が0.8〜20の、非晶質ケイ酸カルシウム水和物単体、または該水和物とCa(OH)の複合物を用いて排水中のリンを回収する方法が提案されている。
As a phosphorus recovery material that solves this problem, Patent Document 4 proposes a porous calcium silicate hydrate having an average particle diameter of 150 μm or less and a pore volume of 0.3 cm 3 / g or more. Proposes a porous and amorphous calcium silicate hydrate having an average particle size of 10 μm to 150 μm, a BET specific surface area of 80 m 2 / g or more, and a pore volume of 0.5 cm 3 / g or more. .
Further, in Patent Document 6, Ca (OH) 2 is 2.5 to 80 wt%, Ca / Si molar ratio is 1.0 to 7.0, and amorphous calcium silicate hydrate and Ca (OH). A phosphorus recovery material comprising a composite of 2 has been proposed. The phosphorus recovery material is excellent in the performance of adsorbing phosphorus, and the composite adsorbing phosphorus has a high sedimentation property, so that it has a high phosphorus removal effect and can shorten the processing time (paragraph 0009).
Furthermore, in Patent Document 7, drainage is performed using amorphous calcium silicate hydrate alone or a composite of the hydrate and Ca (OH) 2 having a Ca / Si molar ratio of 0.8 to 20. A method for recovering the phosphorus in it has been proposed.

特開昭61−263636号公報JP-A 61-263636 特公平02−020315号公報Japanese Examined Patent Publication No. 02-020315 特開平10−235344号公報JP-A-10-235344 特開2009−285635号公報JP 2009-285635 A 特開2009−285636号公報JP 2009-285636 A 特開2012−50975号公報JP 2012-50975 A 特開2013−27865号公報JP 2013-27865 A

本発明は、前記特許文献6で提案されたリン回収材の利点を有し、さらに肥料効果が高いリン回収用資材等を提供することを目的とする。   An object of the present invention is to provide a phosphorus recovery material and the like that have the advantages of the phosphorus recovery material proposed in Patent Document 6 and have a high fertilizer effect.

本発明者は、前記目的にかなうリン回収用資材を検討したところ、下記のリン回収用資材は前記目的にかなうことを見い出し、本発明を完成させた。すなわち、本発明は、下記の構成を有するリン回収用資材、その製造方法、およびリン回収方法である。
[1]石灰と下記(1)のシリカとを混合して生成してなる、下記(2)の非晶質珪酸カルシウム水和物単体または非晶質珪酸カルシウム水和物とCa(OH)との複合物を含む、リン回収用資材。
(1)加熱処理して有機物を除去した易溶解性シリカ含有鉱物と、濃度が1M以上の水酸化アルカリ水溶液とを混合して溶出してなる易溶解性シリカ
(2)Ca/Siのモル比が0.8〜20である、非晶質珪酸カルシウム水和物単体または非晶質珪酸カルシウム水和物とCa(OH)との複合物
[2]リン回収用資材中のカルシウムとリン含有水中のリンの含有量が、Ca/Pのモル比で2.0になるように混合した場合のリン回収率が70%以上である、前記[1]に記載のリン回収用資材。
[3]リンを吸着して回収したリン回収用資材のく溶性りん酸濃度が15%以上である、前記[1]または[2]に記載のリン回収用資材。
[4]前記[1]〜[3]のいずれかに記載のリン回収用資材の製造方法であって、下記の(A)工程〜(D)工程を少なくとも含む、リン回収用資材の製造方法。
(A)易溶解性シリカ含有鉱物を加熱して、該鉱物中の有機物を熱分解して除く、易溶解性シリカ含有鉱物の加熱処理工程
(B)前記加熱処理した易溶解性シリカ含有鉱物と、濃度が1M以上の水酸化アルカリ水溶液を混合して撹拌し、該鉱物中の易溶解性シリカを溶出させる、易溶解性シリカの溶出工程
(C)前記易溶解性シリカの溶出液と酸を混合してpHを調整し、溶解していた不純物を析出させた後、該溶出液を固液分離して前記析出した不純物を除くことにより、易溶解性シリカの溶出液を精製する、易溶解性シリカの精製工程
(D)前記精製した易溶解性シリカの溶出液に対し、水を添加してシリカの濃度を調整した後、石灰中のCaと前記精製した易溶解性シリカの溶出液中のSiのCa/Siのモル比が0.8〜20になるように、該溶出液と石灰を混合して撹拌し非晶質珪酸カルシウム水和物を生成させ、非晶質珪酸カルシウム水和物単体または非晶質珪酸カルシウム水和物とCa(OH)との複合物のスラリーを得る、スラリーの作製工程
[5]リン含有水と、前記[1]〜[3]のいずれかに記載のリン回収用資材とを混合した後、リンを吸着してなるリン回収用資材を得る、リン回収方法。
The inventor has examined phosphorus recovery materials that meet the above-mentioned object, and found that the following phosphorus recovery materials can meet the above-mentioned object, thereby completing the present invention. That is, this invention is the phosphorus collection | recovery material which has the following structure, its manufacturing method, and a phosphorus collection | recovery method.
[1] Amorphous calcium silicate hydrate alone or amorphous calcium silicate hydrate of the following (2) formed by mixing lime and silica of (1) below and Ca (OH) 2 Phosphorus recovery materials, including composites.
(1) Easily soluble silica obtained by mixing and eluting an easily soluble silica-containing mineral from which organic substances have been removed by heat treatment and an aqueous alkali hydroxide solution having a concentration of 1 M or more (2) molar ratio of Ca / Si 0.8-20, amorphous calcium silicate hydrate alone or a composite of amorphous calcium silicate hydrate and Ca (OH) 2
[2] The phosphorus recovery rate is 70% or more when the calcium content in the phosphorus recovery material and the phosphorus content in the phosphorus-containing water are mixed so that the molar ratio of Ca / P is 2.0. The material for recovering phosphorus according to [1].
[3] The phosphorus recovery material according to [1] or [2], wherein the phosphorus recovery material recovered by adsorbing phosphorus has a soluble phosphoric acid concentration of 15% or more.
[4] A method for producing a phosphorus recovery material according to any one of [1] to [3], comprising at least the following steps (A) to (D): .
(A) A heat-treating step of a readily soluble silica-containing mineral by heating the easily soluble silica-containing mineral to thermally decompose and remove organic matter in the mineral (B) The heat-treated easily soluble silica-containing mineral and , An elution step of easily soluble silica in which an alkali hydroxide aqueous solution having a concentration of 1M or more is mixed and stirred to elute the readily soluble silica in the mineral. After adjusting the pH by mixing and precipitating the dissolved impurities, the eluate is purified by solid-liquid separation to remove the precipitated impurities, thereby easily dissolving the eluate of easily soluble silica. (D) After adjusting the concentration of silica by adding water to the eluate of the purified easily soluble silica, Ca in lime and the eluate of the purified easily soluble silica The Ca / Si molar ratio of Si is 0.8-20. As described above, by mixing the eluate with lime to produce a stirring amorphous calcium silicate hydrate, amorphous calcium silicate hydrate alone or amorphous calcium silicate hydrate and Ca (OH) 2 A slurry production process for obtaining a slurry of a composite with
[5] A phosphorus recovery method for obtaining a phosphorus recovery material obtained by adsorbing phosphorus after mixing phosphorus-containing water and the phosphorus recovery material according to any one of [1] to [3].

本発明のリン回収用資材はリンの回収率が高く、また、リンを吸着して回収した後のリン回収用資材は、く溶性りん酸濃度が高い。したがって、本発明のリン回収用資材は、下水処理場等で発生するリン含有水中からリンを回収して、りん酸質肥料を製造するための資材として好適である。   The phosphorus recovery material of the present invention has a high phosphorus recovery rate, and the phosphorus recovery material after adsorbing and recovering phosphorus has a high soluble phosphoric acid concentration. Therefore, the phosphorus recovery material of the present invention is suitable as a material for recovering phosphorus from phosphorus-containing water generated at a sewage treatment plant or the like to produce a phosphate fertilizer.

実施例において用いた珪質頁岩(易溶解性シリカ含有鉱物)の粉末X線回折ピークを示す図である。It is a figure which shows the powder X-ray-diffraction peak of the siliceous shale (easily soluble silica containing mineral) used in the Example. 実施例における本発明のリン回収用資材の製造方法を示すフロー図である。It is a flowchart which shows the manufacturing method of the phosphorus collection | recovery material of this invention in an Example.

以下、本発明をリン回収用資材、その製造方法、およびリン回収方法に分けて説明する。
1.リン回収用資材
本発明のリン回収用資材は、石灰と易溶性シリカとを混合して生成した非晶質珪酸カルシウム水和物単体(以下「CSH」という。)、またはCSHとCa(OH)との複合物(以下「CSH複合物」という。)である。
ここで、CSHとは、珪酸カルシウム水和物の内、結晶性とされるトバモライト(tobermorite)やゾノトライト(xonotlite)を除いたものをいう。また、CSH複合物とは、CSHが、余剰の石灰から生じるCa(OH)を取り込むことにより生成する複合物であって、Ca(OH)がCSHの内部に分散した状態で存在する複合物である。そして、該複合物はCSHとCa(OH)を単に混合してなる混合物とは異なる物質であり、該複合物の沈降性は該混合物の沈降性と比べ高い。
Hereinafter, the present invention will be described by dividing it into phosphorus recovery materials, manufacturing methods thereof, and phosphorus recovery methods.
1. Phosphorus Recovery Material The phosphorus recovery material of the present invention is an amorphous calcium silicate hydrate simple substance (hereinafter referred to as “CSH”) formed by mixing lime and readily soluble silica, or CSH and Ca (OH). 2 (hereinafter referred to as “CSH composite”).
Here, CSH refers to calcium silicate hydrate excluding crystalline tobermorite and xonotlite. The CSH composite is a composite that CSH is generated by taking in Ca (OH) 2 generated from excess lime, and is a composite in which Ca (OH) 2 is dispersed inside CSH. It is a thing. The composite is a substance different from a mixture obtained by simply mixing CSH and Ca (OH) 2 , and the sedimentation property of the composite is higher than the sedimentation property of the mixture.

また、前記易溶性シリカは、易溶解性シリカ含有鉱物を加熱処理して有機物を除去した後に、濃度が1M以上の水酸化アルカリ水溶液と混合して溶出してなるシリカである。有機物を除去した易溶解性シリカ含有鉱物は、有機物を除去していない易溶解性シリカ含有鉱物と比べ、製造したリン回収用資材に含まれる有機物が少ないため、処理対象となるリン含有水へ有機物が溶出する懸念がなく、BODやCODが増加しないという利点がある。また、1M以上の水酸化アルカリ水溶液を用いると、易溶性シリカの溶出速度が大きくなる。なお、水酸化アルカリ水溶液の濃度は、好ましくは2M以上である。
前記易溶解性シリカ含有鉱物は、常圧条件で、好ましくは30℃以上に加熱した条件で、アルカリ溶液に溶解するアルカリ可溶性シリカを含むシリカ材料である。易溶解性シリカ原料として例えば、珪質頁岩、アモルファスシリカ、シリカゲル、シリカフューム、オパールおよび珪藻土からなる群より選ばれる1種以上が挙げられる。
また、前記水酸化アルカリは、水酸化ナトリウム、水酸化カリウム、および水酸化リチウム等からなる群より選ばれる1種以上である。
前記石灰は、消石灰、生石灰、水酸化カルシウム、および酸化カルシウムからなる群より選ばれる1種以上である。
The readily soluble silica is a silica obtained by elution by mixing an easily soluble silica-containing mineral with a 1 M or higher alkali hydroxide aqueous solution after removing organic substances by heat treatment. The easily soluble silica-containing mineral from which organic matter has been removed has less organic matter contained in the produced phosphorus recovery material than the readily soluble silica-containing mineral from which organic matter has not been removed, so the organic matter is added to the phosphorus-containing water to be treated. There is no concern about elution, and there is an advantage that BOD and COD do not increase. Moreover, when 1 M or more of alkali hydroxide aqueous solution is used, the elution rate of easily soluble silica will become large. The concentration of the aqueous alkali hydroxide solution is preferably 2M or more.
The readily soluble silica-containing mineral is a silica material containing alkali-soluble silica that dissolves in an alkali solution under normal pressure conditions, preferably under heating at 30 ° C. or higher. Examples of the readily soluble silica material include one or more selected from the group consisting of siliceous shale, amorphous silica, silica gel, silica fume, opal, and diatomaceous earth.
The alkali hydroxide is at least one selected from the group consisting of sodium hydroxide, potassium hydroxide, lithium hydroxide and the like.
The lime is at least one selected from the group consisting of slaked lime, quick lime, calcium hydroxide, and calcium oxide.

前記CSHまたはCSH複合物中のCa/Siのモル比は0.8〜20である。該モル比が0.8未満ではリンの吸着が十分ではなく、20を超えると水酸化カルシウムが過剰になり、沈降性が低下する。なお、前記Ca/Siのモル比は、好ましくは0.9〜15、より好ましくは1.0〜10である。ちなみに、前記CSH複合物中のCa(OH)の含有率は、Ca/Siのモル比が1.5では約10質量%、5.5では約50質量%、10では約62質量%、20では約86質量%である。 The molar ratio of Ca / Si in the CSH or CSH composite is 0.8-20. When the molar ratio is less than 0.8, phosphorus is not sufficiently adsorbed. When the molar ratio exceeds 20, calcium hydroxide becomes excessive and sedimentation properties decrease. The molar ratio of Ca / Si is preferably 0.9 to 15, more preferably 1.0 to 10. Incidentally, the content ratio of Ca (OH) 2 in the CSH composite is about 10% by mass when the molar ratio of Ca / Si is 1.5, about 50% by mass at 5.5, and about 62% by mass at 10. 20 is about 86% by mass.

また、本発明のリン回収用資材のリン回収率は、該資材中のカルシウムとリン含有水中のリンの含有量が、Ca/Pのモル比で2.0になるように混合した場合、好ましくは70%以上であり、より好ましくは90%以上である。該値が70%以上であれば、リン含有水中のリンを効率よく回収できる。なお、リン回収率は下記式により算出する。
R=100×(P−P)/P
ただし、式中、Rはリン回収率(%)を表し、Pはリン回収用資材を添加する前のリン含有水中のリン濃度(mg/L)を表し、Pはリン回収用資材を添加してリンを吸着して回収した後にリン含有水をろ過して得たろ液中のリン濃度(mg/L)を表す。
Further, the phosphorus recovery rate of the phosphorus recovery material of the present invention is preferably when the calcium content in the material and the phosphorus content in the phosphorus-containing water are mixed so that the molar ratio of Ca / P is 2.0. Is 70% or more, more preferably 90% or more. If this value is 70% or more, phosphorus in phosphorus-containing water can be efficiently recovered. The phosphorus recovery rate is calculated by the following formula.
R = 100 × (P 0 −P) / P 0
In the formula, R represents the phosphorus recovery rate (%), P 0 represents the phosphorus concentration (mg / L) in the phosphorus-containing water before adding the phosphorus recovery material, and P added the phosphorus recovery material. The phosphorus concentration (mg / L) in the filtrate obtained by filtering phosphorus-containing water after adsorbing and recovering phosphorus is expressed.

また、リンを吸着して回収した後のリン回収用資材のく溶性りん酸濃度は、好ましくは15%以上、より好ましくは20%以上である。該値が15%以上であれば、該資材を肥料効果の高いりん酸質肥料として利用することができる。ちなみに、肥料取締法に基づいて定められた普通肥料の公定規格(昭和61年2月22日・農林水産省告示第284号)では、副産りん酸肥料のく溶性りん酸濃度は15%以上と規定されている。   Moreover, the soluble phosphoric acid concentration of the material for recovering phosphorus after adsorbing and recovering phosphorus is preferably 15% or more, more preferably 20% or more. If the value is 15% or more, the material can be used as a phosphate fertilizer having a high fertilizer effect. By the way, according to the official standard of ordinary fertilizer established based on the Fertilizer Control Law (February 22, 1986, Ministry of Agriculture, Forestry and Fisheries Notification No. 284), by-product phosphate fertilizer has a soluble phosphate concentration of 15% or more. It is prescribed.

2.リン回収用資材の製造方法
該製造方法は、(A)易溶解性シリカ含有鉱物の加熱処理工程、(B)易溶解性シリカの溶出工程(C)易溶解性シリカの精製工程、および(D)スラリーの作製工程を少なくとも含む製造方法である。以下に(A)工程〜(D)工程に分けて説明する。
2. Method for Producing Phosphorus Recovery Material The production method comprises (A) a heat treatment step for a readily soluble silica-containing mineral, (B) an elution step for easily soluble silica, (C) a purification step for easily soluble silica, and (D ) A manufacturing method including at least a slurry preparation step. Hereinafter, the steps (A) to (D) will be described separately.

(A)易溶解性シリカ含有鉱物の加熱処理工程
該工程は、易溶解性シリカ含有鉱物(その粉砕物も含む。)を、電気炉やロータリーキルン等の加熱装置を用いて加熱して、該鉱物中の有機物を熱分解して除く工程である。有機物を除いた易溶解性シリカ含有鉱物は、製造したリン回収用資材に含まれる有機物が少ないため、処理対象となるリン含有水へ有機物が溶出する懸念がなく、BODやCODが増加しないという利点がある。
前記加熱温度は、好ましくは400℃以上、より好ましくは500℃以上、さらに好ましくは600℃以上であり、その上限は1000℃である。該値が400℃未満では、加熱処理に時間がかかり、1000℃を超えると易溶性シリカが減少する傾向がある。
また、加熱時間は前記鉱物の粒度にもよるが、好ましくは1時間以上、より好ましくは2時間以上、さらに好ましくは3時間以上である。
また、前記加熱処理後の有機物の含有率は、好ましくは5質量%以下、より好ましくは3質量%以下、さらに好ましくは1質量%以下である。
(A) Heat-treating step of easily soluble silica-containing mineral This step heats easily-soluble silica-containing mineral (including pulverized product thereof) using a heating device such as an electric furnace or a rotary kiln, It is a process of removing organic matter inside by thermal decomposition. Easily soluble silica-containing minerals, excluding organic matter, have the advantage that organic matter is not contained in the phosphorus-containing water to be treated because there is little organic matter contained in the produced phosphorus recovery material, and BOD and COD do not increase There is.
The heating temperature is preferably 400 ° C. or higher, more preferably 500 ° C. or higher, still more preferably 600 ° C. or higher, and the upper limit is 1000 ° C. When the value is less than 400 ° C., the heat treatment takes time, and when it exceeds 1000 ° C., the readily soluble silica tends to decrease.
The heating time depends on the particle size of the mineral, but is preferably 1 hour or longer, more preferably 2 hours or longer, and further preferably 3 hours or longer.
The content of the organic matter after the heat treatment is preferably 5% by mass or less, more preferably 3% by mass or less, and still more preferably 1% by mass or less.

(B)易溶解性シリカの溶出工程
該工程は、前記加熱処理した易溶解性シリカ含有鉱物と、濃度が1M以上の水酸化アルカリ水溶液を混合して撹拌し、該鉱物中の易溶解性シリカを溶出させる工程である。
濃度が1M以上の水酸化アルカリ水溶液を用いると、易溶性シリカの溶出速度が大きくなり、またその溶出量が多くなる。水酸化アルカリ水溶液の混合量は、易溶解性シリカ含有鉱物中の易溶解性シリカの含有量にも依るが、好ましくは易溶解性シリカ含有鉱物100質量部に対し、水酸化アルカリ水溶液を100〜3000質量部である。
前記混合・撹拌時の水溶液の温度は、常温でもよいが、作業効率等をさらに高めるためには、好ましくは50℃以上、より好ましくは60℃以上、さらに好ましくは70℃以上である。該値が50℃以上であれば、易溶解性シリカの溶出速度が格段に大きくなる。
また、前記撹拌時間は、前記水溶液の温度にもよるが、好ましくは30分以上、より好ましくは1時間以上である。
(B) Elution process of easily soluble silica The process comprises mixing the heat-treated easily soluble silica-containing mineral and an alkali hydroxide aqueous solution having a concentration of 1M or more and stirring the easily soluble silica in the mineral. Is a step of eluting.
When an aqueous alkali hydroxide solution having a concentration of 1 M or more is used, the elution rate of readily soluble silica increases and the amount of elution increases. The mixing amount of the aqueous alkali hydroxide solution depends on the content of the easily soluble silica in the easily soluble silica-containing mineral, but preferably 100 to 100 parts by weight of the easily soluble silica-containing mineral contains 100 to 100 parts of the alkali hydroxide aqueous solution. 3000 parts by mass.
The temperature of the aqueous solution at the time of mixing and stirring may be room temperature, but is preferably 50 ° C. or higher, more preferably 60 ° C. or higher, and further preferably 70 ° C. or higher in order to further improve working efficiency. When the value is 50 ° C. or higher, the elution rate of the readily soluble silica is remarkably increased.
Moreover, although the said stirring time is based also on the temperature of the said aqueous solution, Preferably it is 30 minutes or more, More preferably, it is 1 hour or more.

(C)易溶解性シリカの精製工程
前記易溶解性シリカの溶出液と酸を混合してpHを調整し、溶解していた不純物を析出させた後、該溶出液を固液分離して前記析出した不純物を除くことにより、易溶解性シリカの溶出液を精製する工程である。
前記酸は、硫酸、塩酸、硝酸等の無機酸からなる群より選ばれる1種以上が挙げられる。
また前記pHの範囲は、溶解していたアルミニウムや鉄等の不純物が析出するpHの範囲であり、好ましくは8〜13、より好ましくは9〜12、さらに好ましくは10〜11である。液中に存在するアルミニウムや鉄等の不純物は、リン酸塩との間で難溶性の塩を形成して、本来、リン回収用資材が吸着すべきリン含有水中のリンが減少するほか、リンを吸着して回収したリン回収用資材をりん酸質肥料として用いた場合、く溶性りん濃度が低いため肥料効果が低い。
また、前記固液分離の手段は、ろ過、吸引ろ過、デカンテーション、遠心分離等が挙げられる。
(C) Purification step of easily soluble silica The eluate of the easily soluble silica and an acid are mixed to adjust the pH, and the dissolved impurities are precipitated, and then the eluate is separated into solid and liquid. This is a step of purifying the eluate of readily soluble silica by removing the precipitated impurities.
Examples of the acid include one or more selected from the group consisting of inorganic acids such as sulfuric acid, hydrochloric acid, and nitric acid.
Moreover, the range of the said pH is the range of the pH from which impurities, such as dissolved aluminum and iron, precipitate, Preferably it is 8-13, More preferably, it is 9-12, More preferably, it is 10-11. Impurities such as aluminum and iron present in the liquid form a sparingly soluble salt with the phosphate, reducing the phosphorus in the phosphorus-containing water that should be adsorbed by the phosphorus recovery material. When the material for recovering phosphorus collected by adsorbing is used as phosphate fertilizer, the fertilizer effect is low because the soluble phosphorus concentration is low.
Examples of the solid-liquid separation means include filtration, suction filtration, decantation, and centrifugal separation.

(D)スラリーの作製工程
前記精製した易溶解性シリカの溶出液に対し、水を添加してシリカの濃度を調整した後、石灰中のCaと前記精製した易溶解性シリカの溶出液中のSiのCa/Siのモル比が0.8〜20になるように、該溶出液に石灰を添加し撹拌してCSHを生成させ、CSHまたはCSH複合物のスラリーを得る工程である。
前記シリカの濃度は、好ましくは、易溶解性シリカの溶出液中のシリカ(SiO)濃度が5質量%以下に調整する。該値が5質量%を超えると、石灰を混合した際に、前記溶出液がゲル化して攪拌が困難になり、CSH等の組成が不均一になるおそれがある。
前記石灰は、易溶解性シリカの溶出液との混合の際に不均一にならないようにスラリーにして混合するとよい。
(D) Slurry preparation process After adjusting the concentration of silica by adding water to the purified eluate of the easily soluble silica, Ca in lime and the eluate of the purified easily soluble silica In this process, lime is added to the eluate and stirred to produce CSH so that the molar ratio of Si to Ca / Si is 0.8 to 20, thereby obtaining a slurry of CSH or CSH composite.
The concentration of the silica is preferably adjusted so that the silica (SiO 2 ) concentration in the eluent of easily soluble silica is 5% by mass or less. When the value exceeds 5% by mass, when the lime is mixed, the eluate is gelled and stirring becomes difficult, and the composition of CSH and the like may become nonuniform.
The lime is preferably mixed in a slurry so as not to become non-uniform when mixed with the eluent of readily soluble silica.

本発明のリン回収用資材の製造方法は、前記(A)工程〜(D)工程を必須の工程として含むほか、以下の(E)CSHまたはCSH複合物の乾燥工程を任意の工程として含むこともできる。すなわち、本発明のリン回収用資材として、前記(D)工程により得られたCSHまたはCSH複合物のスラリーを用いてもよく、これを乾燥したCSHまたはCSH複合物の乾燥物(粉体または粒体等)を用いてもよい。そこで、本発明のリン回収用資材として乾燥物を用いる場合、本発明のリン回収用資材の製造方法は、さらに、下記の(E)工程を任意の工程として含むことになる。   The method for producing a phosphorus recovery material of the present invention includes the steps (A) to (D) as essential steps, and also includes the following (E) drying step of CSH or CSH composite as an optional step. You can also. That is, as the phosphorus recovery material of the present invention, the CSH or CSH composite slurry obtained in the step (D) may be used, and the dried CSH or CSH composite dried product (powder or granules) Body etc.) may be used. Then, when using a dried material as the phosphorus collection | recovery material of this invention, the manufacturing method of the phosphorus collection | recovery material of this invention further includes the following (E) process as an arbitrary process.

(E)CSHまたはCSH複合物の乾燥工程
該工程は、前記スラリー、または前記スラリーからろ過等により不純物を除いた液を乾燥して、CSHまたはCSH複合物の乾燥物を得る工程である。乾燥により、本発明のリン回収用資材は保管や運搬がより容易になる。また、乾燥物が塊状で得られる場合は、粉体や粒体にするために粉砕や磨砕等を行ってもよい。
(E) Drying step of CSH or CSH composite This step is a step of obtaining a dried product of CSH or CSH composite by drying the slurry or a liquid obtained by removing impurities from the slurry by filtration or the like. Drying makes the phosphorus recovery material of the present invention easier to store and transport. In addition, when the dried product is obtained in the form of a lump, it may be pulverized or ground to obtain a powder or granule.

3.リン回収方法
該回収方法は、リン含有水と、前記リン回収用資材(CSHまたはCSH複合物)とを混合した後、リンを吸着したリン回収用資材を得る方法である。ここで、リン含有水は、特に限定されず、下水汚泥離脱液、リンを含む工場廃液等が挙げられる。
前記リン回収用資材は、スラリーまたは乾燥物の態様でリンの回収に用いることができるが、リン回収用資材を粉体の態様で用いると均一に混ざらない場合は、好ましくは該粉体を予めスラリーにして用いる。
リンを吸着したリン回収用資材は、ろ過、沈降分離、または遠心分離等により分離して回収する。ここで回収したリン回収用資材は、段落0029に記載したように、く溶性りん濃度が高いため、りん酸質肥料またはその原料として好適である。
3. Phosphorus Recovery Method The recovery method is a method for obtaining phosphorus-recovered material that adsorbs phosphorus after mixing phosphorus-containing water and the phosphorus-recovery material (CSH or CSH composite). Here, the phosphorus-containing water is not particularly limited, and examples thereof include sewage sludge separation liquid and factory waste liquid containing phosphorus.
The phosphorus recovery material can be used for recovery of phosphorus in the form of a slurry or a dried product. However, if the phosphorus recovery material is not uniformly mixed when used in the form of a powder, the powder is preferably preliminarily mixed. Use as a slurry.
The phosphorus recovery material adsorbing phosphorus is separated and recovered by filtration, sedimentation separation, or centrifugation. The phosphorus recovery material recovered here is suitable as a phosphate fertilizer or a raw material thereof because it has a high soluble phosphorus concentration as described in paragraph 0029.

以下、本発明を実施例により説明するが、本発明はこれらの実施例に限定されない。
1.使用材料
(1)易溶解性シリカ含有鉱物
北海道産の珪質頁岩(化学組成:SiO 80質量%、Al 10質量%、Fe 5質量%)
(2)水酸化ナトリウム
試薬1級(関東化学社製)
(3)消石灰
JIS R 9001:2006に規定する特号消石灰(薬仙石灰社製)
EXAMPLES Hereinafter, although an Example demonstrates this invention, this invention is not limited to these Examples.
1. Materials used (1) Easily soluble silica-containing minerals Silica shale from Hokkaido (chemical composition: SiO 2 80 mass%, Al 2 O 3 10 mass%, Fe 2 O 3 5 mass%)
(2) Sodium hydroxide reagent grade 1 (manufactured by Kanto Chemical Co., Inc.)
(3) Slaked lime Special slaked lime as defined in JIS R 9001: 2006 (manufactured by Yakusen Lime)

2.リン回収用資材の製造
下記(A)〜(E)の工程を経て、実施例のリン回収用資材を製造した。なお、図2に、製造方法のフロー図を示す。
(A)易溶解性シリカ含有鉱物の加熱処理工程
珪質頁岩の粉砕物250gを電気炉に入れて600℃で3時間加熱し、珪質頁岩中の有機物を熱分解して除いた。
(B)易溶解性シリカの溶出工程
前記加熱処理した珪質頁岩に2Mの水酸化ナトリウム水溶液1000gを添加した後、70℃に加温して1時間撹拌し、珪質頁岩中の易溶解性シリカを溶出させた。
(C)易溶解性シリカの精製工程
前記易溶解性シリカの溶出液に硫酸を添加してpH10.5に調整し、溶出していたアルミニウムや鉄等の不純物を析出させた後、該溶出液をろ紙を用いた吸引ろ過により前記析出物を含む不溶物を固液分離して除き、易溶解性シリカの溶出液を精製した。
(D)スラリーの作製工程
前記精製した易溶解性シリカの溶出液1000gに対し、蒸留水2000gを添加して、シリカの濃度を3.3質量%に調整した。次に、消石灰中のCaと前記精製した易溶解性シリカの溶出液中のCa/Siのモル比が1.0になるように、該溶出液に消石灰120gを添加し、常温で1時間撹拌してCSHを生成させ、該CSHのスラリーを得た。
(E)CSHの乾燥工程
前記スラリーを吸引ろ過して得た液を105℃で24時間乾燥して、CSHの乾燥物の粉末(以下「リン回収用資材A」という。)を得た。
2. Manufacture of phosphorus recovery material The phosphorus recovery material of the example was manufactured through the following steps (A) to (E). FIG. 2 shows a flowchart of the manufacturing method.
(A) Heat treatment process of easily soluble silica-containing mineral 250 g of crushed siliceous shale was placed in an electric furnace and heated at 600 ° C. for 3 hours to thermally decompose and remove organic matter in the siliceous shale.
(B) Elution process of easily soluble silica After adding 1000 g of 2M sodium hydroxide aqueous solution to the heat-treated siliceous shale, the mixture was heated to 70 ° C. and stirred for 1 hour to easily dissolve in the siliceous shale. Silica was eluted.
(C) Purification step of readily soluble silica After adding sulfuric acid to the eluate of the easily soluble silica to adjust the pH to 10.5 and precipitating impurities such as aluminum and iron that had been eluted, the eluate The insoluble matter containing the precipitate was removed by solid-liquid separation by suction filtration using filter paper, and the eluate of readily soluble silica was purified.
(D) Slurry production process 2000 g of distilled water was added to 1000 g of the eluate of the purified readily soluble silica to adjust the concentration of silica to 3.3% by mass. Next, 120 g of slaked lime is added to the eluate so that the Ca / Si molar ratio of Ca in the slaked lime and the purified easily soluble silica eluate is 1.0, and the mixture is stirred at room temperature for 1 hour. CSH was produced to obtain a slurry of the CSH.
(E) CSH Drying Step A liquid obtained by suction filtration of the slurry was dried at 105 ° C. for 24 hours to obtain a dry powder of CSH (hereinafter referred to as “phosphorus recovery material A”).

また、特許文献6に記載のリン回収材(リン回収用資材)を比較例に用いるために、特許文献6の段落0030に記載の方法に準じて回収用資材を製造した。すなわち、特許文献6の段落0030に記載の方法は、前記リン回収用資材Aの製造方法において、(A)珪質頁岩の加熱処理工程と、(C)易溶解性シリカの精製工程を省いた方法である。具体的には、下記(i)〜(iii)工程を経て、前記比較例のリン回収用資材を製造した。
(i)易溶解性シリカの溶出工程
0.125Mの水酸化ナトリウム水溶液1000gを70℃に加温した後、これに加熱処理をしていない珪質頁岩の粉砕物250gを添加して70℃で1時間撹拌し、珪質頁岩中の易溶解性シリカを溶出させて易溶解性シリカの溶出液を得た。
(ii)CSHの水熱合成工程
Ca/Siのモル比が1.0になるように、70℃に維持された前記溶出液に消石灰を添加した後、70℃で1時間撹拌して水熱合成により非晶質ケイ酸カルシウム水和物を生成させ、CSHのスラリーを得た。
(iii)CSHの乾燥工程
前記CSHのスラリーをデカンテーションして不溶物と前記CSHを含む上澄み液を分離し、該CSHを含む上澄み液を105℃で24時間乾燥して、CSHの乾燥物の粉末(以下「リン回収用資材B」という。)を得た。
リン回収用資材A中とリン回収用資材B中のアルミニウムと鉄の含有率を比較すると、アルミニウムの含有率はそれぞれ0.1質量%と4.3質量%、鉄の含有率はそれぞれ0.05質量%と1.1質量%、炭素の含有率はそれぞれ0.005質量%と0.2質量%であるから、リン回収用資材Aはリン回収用資材Bと比べ、アルミニウム等の不純物の量が1/10以下と格段に少ないことが分かる。
Moreover, in order to use the phosphorus collection | recovery material (phosphorus collection | recovery material) of patent document 6 for a comparative example, the collection material was manufactured according to the method of paragraph 0030 of patent document 6. FIG. That is, the method described in Paragraph 0030 of Patent Document 6 omits (A) the heat treatment step of siliceous shale and (C) the purification step of readily soluble silica in the method for producing phosphorus recovery material A. Is the method. Specifically, the phosphorus recovery material of the comparative example was manufactured through the following steps (i) to (iii).
(I) Elution process of easily soluble silica After heating 1000 g of 0.125M sodium hydroxide aqueous solution to 70 ° C., 250 g of crushed siliceous shale not heated was added thereto at 70 ° C. The mixture was stirred for 1 hour, and the readily soluble silica in the siliceous shale was eluted to obtain an easily soluble silica eluate.
(ii) Hydrothermal synthesis step of CSH After adding slaked lime to the eluate maintained at 70 ° C. so that the Ca / Si molar ratio is 1.0, the mixture is stirred for 1 hour at 70 ° C. and hydrothermal. Amorphous calcium silicate hydrate was produced by synthesis to obtain a slurry of CSH.
(Iii) CSH drying step The CSH slurry is decanted to separate the insoluble matter and the supernatant containing the CSH, and the supernatant containing the CSH is dried at 105 ° C. for 24 hours. A powder (hereinafter referred to as “phosphorus recovery material B”) was obtained.
Comparing the contents of aluminum and iron in the phosphorus recovery material A and phosphorus recovery material B, the aluminum content is 0.1% by mass and 4.3% by mass, respectively, and the iron content is 0.00%. Since the content of carbon is 05% by mass and 1.1% by mass, and the carbon content is 0.005% by mass and 0.2% by mass, respectively, the phosphorus recovery material A is less in impurities such as aluminum than the phosphorus recovery material B. It can be seen that the amount is significantly less than 1/10.

2.リン回収試験
PO−P濃度が100mg/Lの下水汚泥脱離液(リン含有水)中に、リン回収用資材Aおよびリン回収用資材Bを、各資材中のカルシウムと汚泥脱離液中のリンの含有量がCa/Pのモル比で2.0になるようにスラリーで添加して常温で1時間撹拌した。1時間経過した後、下水汚泥脱離液中のリンの濃度を、JIS K 0102「工場排水試験法」に規定するモリブデン青吸光光度法に準拠して測定した。その結果を表1に示す。
表1から、実施例および比較例のいずれも、リン回収率は90%以上と高く、優れたリンの回収効果を有している。
2. Phosphorus recovery test Phosphorus recovery material A and phosphorus recovery material B in sewage sludge desorption liquid (phosphorus-containing water) with a PO 4 -P concentration of 100 mg / L in calcium and sludge desorption liquid The phosphorus content was added as a slurry so that the molar ratio of Ca / P was 2.0 and stirred at room temperature for 1 hour. After 1 hour, the concentration of phosphorus in the sewage sludge desorbed liquid was measured according to the molybdenum blue spectrophotometric method prescribed in JIS K 0102 “Factory Wastewater Test Method”. The results are shown in Table 1.
From Table 1, all of the Examples and Comparative Examples have a high phosphorus recovery rate of 90% or more, and have an excellent phosphorus recovery effect.

Figure 2015171696
Figure 2015171696

3.リン回収物中のく溶性りん酸濃度の測定
前記リン回収試験においてリンを吸着して回収してなるリン回収用資材(以下「リン回収物」という。)をろ過して得た後、該リン回収物を105℃で12時間乾燥した。次に、肥料試験法に準拠して、前記乾燥したリン回収物中のく溶性りん酸濃度を測定した。
その結果、く溶性りん酸濃度は、リン回収用資材A由来のリン回収物では20.4%、リン回収用資材B由来のリン回収物では16.8%であった。
以上のことから、リン回収用資材Aおよびリン回収用資材Bのリン回収率は、前記のとおり同等であったにも拘わらず、肥料効果の重要な指標の一つであるく溶性りん酸濃度は、リン回収用資材Aがリン回収用資材Bに比べ、1.2倍高い。したがって、本発明のリン回収用資材は、前記特許文献6で提案されたリン回収用資材よりも、さらに肥料効果が高いといえる。
3. Measurement of the concentration of soluble phosphoric acid in the phosphorus recovery material After the phosphorus recovery material obtained by adsorbing and recovering phosphorus in the phosphorus recovery test (hereinafter referred to as “phosphorus recovery material”) is filtered, The collected material was dried at 105 ° C. for 12 hours. Next, based on the fertilizer test method, the soluble phosphoric acid concentration in the dried phosphorus collection was measured.
As a result, the concentration of soluble phosphoric acid was 20.4% for the phosphorus recovery material derived from the phosphorus recovery material A and 16.8% for the phosphorus recovery material derived from the phosphorus recovery material B.
As described above, the phosphorus recovery rate of the phosphorus recovery material A and the phosphorus recovery material B is the same as described above, but the soluble phosphate concentration is one of the important indicators of the fertilizer effect. The phosphorus recovery material A is 1.2 times higher than the phosphorus recovery material B. Therefore, it can be said that the phosphorus recovery material of the present invention has a higher fertilizer effect than the phosphorus recovery material proposed in Patent Document 6.

Claims (5)

石灰と下記(1)のシリカとを混合して生成してなる、下記(2)の非晶質珪酸カルシウム水和物単体または非晶質珪酸カルシウム水和物とCa(OH)との複合物を含む、リン回収用資材。
(1)加熱処理して有機物を除去した易溶解性シリカ含有鉱物と、濃度が1M以上の水酸化アルカリ水溶液とを混合して溶出してなる易溶解性シリカ
(2)Ca/Siのモル比が0.8〜20である、非晶質珪酸カルシウム水和物単体または非晶質珪酸カルシウム水和物とCa(OH)との複合物
(2) Amorphous calcium silicate hydrate alone or composite of amorphous calcium silicate hydrate and Ca (OH) 2 formed by mixing lime and silica (1) below Material for collecting phosphorus, including waste.
(1) Easily soluble silica obtained by mixing and eluting an easily soluble silica-containing mineral from which organic substances have been removed by heat treatment and an aqueous alkali hydroxide solution having a concentration of 1 M or more (2) molar ratio of Ca / Si 0.8-20, amorphous calcium silicate hydrate alone or a composite of amorphous calcium silicate hydrate and Ca (OH) 2
リン回収用資材中のカルシウムとリン含有水中のリンの含有量が、Ca/Pのモル比で2.0になるように混合した場合のリン回収率が70%以上である、請求項1に記載のリン回収用資材。   The phosphorus recovery rate is 70% or more when the calcium content in the phosphorus recovery material and the phosphorus content in the phosphorus-containing water are mixed so that the molar ratio of Ca / P is 2.0. The phosphorus recovery material described. リンを吸着して回収したリン回収用資材のく溶性りん酸濃度が15%以上である、請求項1または2に記載のリン回収用資材。   The phosphorus recovery material according to claim 1 or 2, wherein the phosphorus recovery material recovered by adsorbing phosphorus has a soluble phosphoric acid concentration of 15% or more. 請求項1〜3のいずれか1項に記載のリン回収用資材の製造方法であって、下記の(A)工程〜(D)工程を少なくとも含む、リン回収用資材の製造方法。
(A)易溶解性シリカ含有鉱物を加熱して、該鉱物中の有機物を熱分解して除く、易溶解性シリカ含有鉱物の加熱処理工程
(B)前記加熱処理した易溶解性シリカ含有鉱物と、濃度が1M以上の水酸化アルカリ水溶液を混合して撹拌し、該鉱物中の易溶解性シリカを溶出させる、易溶解性シリカの溶出工程
(C)前記易溶解性シリカの溶出液と酸を混合してpHを調整し、溶解していた不純物を析出させた後、該溶出液を固液分離して前記析出した不純物を除くことにより、易溶解性シリカの溶出液を精製する、易溶解性シリカの精製工程
(D)前記精製した易溶解性シリカの溶出液に対し、水を添加してシリカの濃度を調整した後、石灰中のCaと前記精製した易溶解性シリカの溶出液中のSiのCa/Siのモル比が0.8〜20.0になるように、該溶出液と石灰を混合して撹拌し非晶質珪酸カルシウム水和物を生成させ、非晶質珪酸カルシウム水和物単体または非晶質珪酸カルシウム水和物とCa(OH)との複合物のスラリーを得る、スラリーの作製工程
It is a manufacturing method of the phosphorus collection | recovery material of any one of Claims 1-3, Comprising: The manufacturing method of the phosphorus collection | recovery material at least including the following (A) process-(D) process.
(A) A heat-treating step of a readily soluble silica-containing mineral by heating the easily soluble silica-containing mineral to thermally decompose and remove organic matter in the mineral (B) The heat-treated easily soluble silica-containing mineral and , An elution step of easily soluble silica in which an alkali hydroxide aqueous solution having a concentration of 1M or more is mixed and stirred to elute the readily soluble silica in the mineral. After adjusting the pH by mixing and precipitating the dissolved impurities, the eluate is purified by solid-liquid separation to remove the precipitated impurities, thereby easily dissolving the eluate of easily soluble silica. (D) After adjusting the concentration of silica by adding water to the eluate of the purified easily soluble silica, Ca in lime and the eluate of the purified easily soluble silica The Ca / Si molar ratio of Si is 0.8-20.0. So that, by mixing the eluate with lime to produce a stirring amorphous calcium silicate hydrate, amorphous calcium silicate hydrate alone or amorphous calcium silicate hydrate and Ca (OH) 2. Slurry production process for obtaining a slurry of a composite with 2
リン含有水と、請求項1〜3のいずれか1項に記載のリン回収用資材とを混合した後、リンを吸着したリン回収用資材を得る、リン回収方法。   The phosphorus collection | recovery method of obtaining the phosphorus collection | recovery material which adsorb | sucked phosphorus, after mixing phosphorus containing water and the phosphorus collection | recovery material of any one of Claims 1-3.
JP2014049113A 2014-03-12 2014-03-12 Material for recovering phosphorus, production method of the material, and method for recovering phosphorus Pending JP2015171696A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2014049113A JP2015171696A (en) 2014-03-12 2014-03-12 Material for recovering phosphorus, production method of the material, and method for recovering phosphorus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2014049113A JP2015171696A (en) 2014-03-12 2014-03-12 Material for recovering phosphorus, production method of the material, and method for recovering phosphorus

Publications (1)

Publication Number Publication Date
JP2015171696A true JP2015171696A (en) 2015-10-01

Family

ID=54259389

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2014049113A Pending JP2015171696A (en) 2014-03-12 2014-03-12 Material for recovering phosphorus, production method of the material, and method for recovering phosphorus

Country Status (1)

Country Link
JP (1) JP2015171696A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2019127413A (en) * 2018-01-24 2019-08-01 太平洋セメント株式会社 Production method of amorphous calcium silicate hydrate
CN113104856A (en) * 2021-05-08 2021-07-13 中南大学 Preparation method, product and application of water body phosphorus removal material

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2019127413A (en) * 2018-01-24 2019-08-01 太平洋セメント株式会社 Production method of amorphous calcium silicate hydrate
CN113104856A (en) * 2021-05-08 2021-07-13 中南大学 Preparation method, product and application of water body phosphorus removal material
CN113104856B (en) * 2021-05-08 2022-11-04 中南大学 Preparation method, product and application of water body phosphorus removal material

Similar Documents

Publication Publication Date Title
Xia et al. Struvite crystallization combined adsorption of phosphate and ammonium from aqueous solutions by mesoporous MgO⿿ loaded diatomite
JP6021199B2 (en) Method for producing phosphate fertilizer
JP5201454B2 (en) Phosphorus recovery material and phosphorus recovery method
CN105419805A (en) Preparing method for complex function repairing agent for treatment of heavy metal contaminated soil
JP5972050B2 (en) Method for producing phosphorus recovery material
WO2012176579A1 (en) Method for recovering phosphorus and using same as fertilizer
CN102115234A (en) Preparation method of flocculant capable of removing phosphate from red mud
JP5930535B2 (en) Phosphorus recovery and fertilizer method
JP5864045B2 (en) Method for producing phosphorus recovery material
CN1765488A (en) Method for preparing absorbent with phosphor concentration and phosphor reclaim function
CN113000025B (en) Phosphorus removal adsorbent and preparation method and application thereof
JP2015171696A (en) Material for recovering phosphorus, production method of the material, and method for recovering phosphorus
CN109231842A (en) A kind of foamed glass material and preparation method thereof reducing water quality total phosphorus index
CN107043146B (en) Method for preparing composite water treatment agent by using cow dung
JP5713735B2 (en) Phosphorus adsorbent and soil conditioner or fertilizer using the same
Huang et al. A comparative study of phosphate removal technologies using adsorption and fluidized bed crystallization process
CN114733486B (en) Preparation method of dephosphorization modified biochar
CN109908860A (en) A kind of phosphorus adsorbent and its application using waterworks sludge preparation
WO2013168245A1 (en) Phosphorous-collecting material, method for producing phosphorous-collecting material, and phosphorous collection method
CN113941312A (en) Aluminum-based phosphorus removal material and preparation method thereof
JP2015196146A (en) Phosphorus recovery material for phosphorus-containing water and phosphorus recovery method using the phosphorus recovery material
Nugroho et al. Removal of Phosphate from Synthetic Aqueous Solution by Adsorption with Dolomite from Padalarang.
JP6381035B2 (en) Method for manufacturing intermediate of phosphorus recovery material and method for manufacturing phosphorus recovery material
JP2016047511A (en) Auxiliary material for recovering phosphorus, and phosphorus recovering method
JP2015091566A (en) Slurry for recovering phosphorus, method for preparing the slurry, and method for recovering phosphorus from phosphorus-containing waste water