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JPS5944895B2 - How to regenerate adsorbent - Google Patents
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JPS5944895B2 - How to regenerate adsorbent - Google Patents

How to regenerate adsorbent

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Publication number
JPS5944895B2
JPS5944895B2 JP17191081A JP17191081A JPS5944895B2 JP S5944895 B2 JPS5944895 B2 JP S5944895B2 JP 17191081 A JP17191081 A JP 17191081A JP 17191081 A JP17191081 A JP 17191081A JP S5944895 B2 JPS5944895 B2 JP S5944895B2
Authority
JP
Japan
Prior art keywords
adsorbent
water
solution
sulfate
regeneration
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
JP17191081A
Other languages
Japanese (ja)
Other versions
JPS5874139A (en
Inventor
尭喜 古森
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.)
Taki Chemical Co Ltd
Original Assignee
Taki Chemical Co 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 Taki Chemical Co Ltd filed Critical Taki Chemical Co Ltd
Priority to JP17191081A priority Critical patent/JPS5944895B2/en
Publication of JPS5874139A publication Critical patent/JPS5874139A/en
Publication of JPS5944895B2 publication Critical patent/JPS5944895B2/en
Expired legal-status Critical Current

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

Description

【発明の詳細な説明】 本発明は吸着剤の再生方法殊に、硫酸根含有水酸化アル
ミニウムあるいはゼオライト質からなる吸着剤の再生方
法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for regenerating an adsorbent, and particularly to a method for regenerating an adsorbent made of sulfate radical-containing aluminum hydroxide or zeolite.

水域の富栄養化物である窒素あるいはりんの除去は甚だ
重要であり、数多くの除去方法が開発されている。
Removal of nitrogen or phosphorus, which are eutrophic substances in water bodies, is extremely important, and many removal methods have been developed.

排水、下水等に含まれるりん酸イオンの吸着剤としては
活性アルミナ、燐酸カルシウム系鉱物あるいは硫酸根含
有水酸化アルミニウムが知られている。
Activated alumina, calcium phosphate minerals, or aluminum hydroxide containing sulfate groups are known as adsorbents for phosphate ions contained in waste water, sewage, etc.

本発明者らは、なかでも硫酸根含有水酸化アルミニウム
がりん酸イオン吸着能が高いことに着目し、これらの再
生方法について、検討を重ねた結果、pH3〜5の硫酸
ナトリウム水溶液で再生しうることを発見し、かかる知
見に基づき本発明を完成したものである。
The present inventors focused on the fact that aluminum hydroxide containing sulfate groups has a high ability to adsorb phosphate ions, and as a result of repeated studies on how to regenerate them, they found that they can be regenerated with an aqueous sodium sulfate solution with a pH of 3 to 5. The present invention was completed based on this finding.

即ち、本発明はpH3〜5の硫酸すl−IJウム水溶液
を用いてりん酸イオンを吸着した硫酸根含有水酸化アル
ミニウムからなる吸着剤の再生方法に関する。
That is, the present invention relates to a method for regenerating an adsorbent made of sulfate group-containing aluminum hydroxide that has adsorbed phosphate ions using an aqueous solution of sodium sulfate having a pH of 3 to 5.

本発明の硫酸根含有水酸化アルミニウムの製造方法とし
ては、硫酸アルミニウム水溶液、あるいはこれら以外の
水可溶性硫酸塩、(例えば、硫酸ナトリウム、硫酸マグ
ネシウム)と水可溶アルミニウム塩(例えば、塩化アル
ミニウム、硝酸アルミニウム、有機酸アルミニウム)の
混合水溶液ニアルカリ金属の水酸化物、炭酸塩、重炭酸
塩、アルミン酸塩等を添加して中和反応により硫酸根含
有水酸化アルミニウムを沈澱せしめる方法、あるいは、
上記の溶液に尿素を加えて尿素を加熱分解することによ
り硫酸根含有水酸化アルミニウムを沈澱せしめる方法が
公知であるが、また本発明吸着剤は、これ単味でも使用
できるが、本発明吸着剤製造時に溶液中にゼオライト、
パーライト、プラスチック球等の担体を分散せしめ、こ
れに本発明吸着剤を沈着、被覆させたものであってもよ
い。
The method for producing the sulfate group-containing aluminum hydroxide of the present invention involves preparing an aqueous aluminum sulfate solution or other water-soluble sulfates (e.g., sodium sulfate, magnesium sulfate) and a water-soluble aluminum salt (e.g., aluminum chloride, nitric acid). A method of precipitating aluminum hydroxide containing sulfate groups through a neutralization reaction by adding a hydroxide, carbonate, bicarbonate, aluminate, etc. of a near-alkali metal to a mixed aqueous solution of aluminum (aluminum, organic acid aluminum), or
A method of precipitating aluminum hydroxide containing sulfate groups by adding urea to the above solution and thermally decomposing the urea is known.Also, the adsorbent of the present invention can be used alone, but the adsorbent of the present invention Zeolite in solution during production,
The adsorbent of the present invention may be deposited and coated on a dispersed carrier such as perlite or plastic spheres.

本発明はこれらの方法により製造されたものに限定され
るものではない。
The present invention is not limited to those produced by these methods.

本発明は上述の如く例えば、排水中のりん酸イオンの除
去に使用された硫酸根含有水酸化アルミニウムからなる
吸着剤の再生にpH3〜5の硫酸すl−IJウム水溶液
を使用するものであるが、このpHの調整には適宜の酸
、例えば硫酸、塩酸、硝酸有機酸等が使用されるが、水
溶液pHが3を下廻ると吸着剤中のアルミニウム分が溶
出し、一方、pH5以上になると再生効果が著しく低下
する。
As mentioned above, the present invention uses a sulfuric acid aqueous solution of pH 3 to 5 to regenerate an adsorbent made of sulfate group-containing aluminum hydroxide used to remove phosphate ions from wastewater, for example. However, to adjust this pH, an appropriate acid such as sulfuric acid, hydrochloric acid, nitric acid, etc. is used. However, when the pH of the aqueous solution is below 3, the aluminum content in the adsorbent is eluted; If this happens, the regeneration effect will be significantly reduced.

而して、硫酸ナトリウム水溶液の濃度としてはNa2S
O4として1〜10重量%の濃度がよく、1%以下では
再生効果が小さく、10重量%を越えても濃度に比例し
た再生効果を期待することができず、経済的でない。
Therefore, the concentration of the sodium sulfate aqueous solution is Na2S
A concentration of 1 to 10% by weight as O4 is preferable; if it is less than 1%, the regeneration effect is small, and even if it exceeds 10% by weight, a regeneration effect proportional to the concentration cannot be expected, which is not economical.

再生方法の態様としては、例えば、吸着剤を充填した充
填塔内に本発明水溶液を流通さしめてもよいし、本発明
水溶液中に吸着剤を加えて緩慢な攪拌後濾過水洗しても
よい。
As an embodiment of the regeneration method, for example, the aqueous solution of the present invention may be passed through a packed column filled with an adsorbent, or the aqueous solution of the present invention may be added to the aqueous solution of the present invention and then slowly stirred and then filtered and washed with water.

要するに本発明水溶液と吸着剤とを公知の任意の方法で
接触せしめれば吸着剤を再生することができる。
In short, the adsorbent can be regenerated by bringing the aqueous solution of the present invention into contact with the adsorbent by any known method.

尚11本発明の硫酸根含有水酸化アルミニウム吸着剤の
再生に0.1NH2S04あるいは0.INNaOHを
使用したときは吸着剤が溶解し再生溶液としては不適で
ありまたNaC1には再生効果が全くない。
11.0.1NH2S04 or 0.1NH2S04 is used to regenerate the sulfate group-containing aluminum hydroxide adsorbent of the present invention. When INNaOH is used, the adsorbent dissolves, making it unsuitable as a regeneration solution, and NaCl has no regeneration effect at all.

一般に下水、工場排水中には、りん酸イオンとアンモニ
ウムイオンが共存している場合が多く、これらの両イオ
ンを除去するためには備酸根含有水酸化アルミニウム及
びゼオライトを別々にあるいは混合したものを塔に充填
し通水すればよい。
In general, sewage and industrial wastewater often contain phosphate ions and ammonium ions, and in order to remove both of these ions, aluminum hydroxide and zeolite containing Bicyl radical can be used separately or in a mixture. All you have to do is fill the tower and pass water through it.

この場合の吸着剤の再生方法として本発明による再生溶
液を使用すれば、吸着剤を一度に再生できるという利点
がある。
If the regeneration solution according to the present invention is used as a method for regenerating the adsorbent in this case, there is an advantage that the adsorbent can be regenerated at once.

さて、本発明再生溶液も使用により次第に濃度が低下す
ると共にりん酸イオン、アンモニウムイオン等の濃度は
上昇するので、漸次再生機能が低下する。
Now, as the regeneration solution of the present invention is used, its concentration gradually decreases, and the concentrations of phosphate ions, ammonium ions, etc. increase, so that the regeneration function gradually decreases.

かかる場合に於ては、この使用済み再生溶液に水酸化ナ
トリウム、炭酸ナトリウムを加えて、アルカリ性とすれ
ばNH4はNH3として揮散し、PO4はカルシウム化
合物等で沈澱除去した後、H2SO4でpHを3〜5に
調整すれば再生溶液を更新することができる。
In such a case, if sodium hydroxide and sodium carbonate are added to the used regeneration solution to make it alkaline, NH4 will be volatilized as NH3, and PO4 will be precipitated and removed with calcium compounds, etc., and then the pH will be adjusted to 3 with H2SO4. The regeneration solution can be renewed by adjusting it to ~5.

他方吸着剤は再生しても徐々に吸着性能は劣化するので
、必要に応じ更新すべきであるが、本発明に於てはこれ
を有効に利用することができる。
On the other hand, even if an adsorbent is regenerated, its adsorption performance gradually deteriorates, so it should be updated as necessary, but this can be effectively utilized in the present invention.

即ち、本発明吸着剤は、これをNaOH溶液に加えて攪
拌しアルミニウム分を溶出させ、カルシウム塩で204
分を分離したのち、この溶液に硫酸あるいは可溶性硫酸
塩を加えて、硫酸根含有水酸化アルミニウムを沈澱させ
れば吸着剤を製造することができる。
That is, the adsorbent of the present invention is prepared by adding it to a NaOH solution and stirring it to elute the aluminum component, and then adding it to a NaOH solution and stirring it to elute the aluminum content.
After separating the components, an adsorbent can be produced by adding sulfuric acid or a soluble sulfate to this solution to precipitate aluminum hydroxide containing sulfate groups.

このように本発明方法によれば、りん酸イオンを簡単に
再生することができまた使用済みの再生溶液は簡単な方
法で更新することができる等本発明方法は多くの利点を
有するものである。
As described above, according to the method of the present invention, phosphate ions can be easily regenerated, and used regenerating solutions can be renewed in a simple manner.The method of the present invention has many advantages. .

以下に本発明の実施例を挙げて説明する。Examples of the present invention will be described below.

実施例 1 硫酸アルミニウム水溶液(A12022係)500gに
攪拌しながら10係炭酸ナトリウム水溶液をpH5,8
になるまで滴下反応させて沈澱物を生成せしめ、濾過水
洗後洗澱物を風乾し、組成A120334.8%、So
、 17.6 %の硫酸根含有水酸化アルミニウムを得
た。
Example 1 A 10% sodium carbonate aqueous solution was added to 500g of aluminum sulfate aqueous solution (A12022) with stirring to pH 5.8.
A precipitate was produced by dropwise reaction until the mixture was filtered, washed with water, and the washed precipitate was air-dried to give a composition of A120334.8%,
, 17.6% of aluminum hydroxide containing sulfate radicals was obtained.

この硫酸根含有水酸化アルミニウム1gを500rfL
lのりん酸アンモニウム水溶液(Po、 50■/l)
に入れて、ゆっくり1時間撹拌し、濾過した後p液中の
PO4濃度を測定した結果3.71ng/ Aであった
1g of this sulfate radical-containing aluminum hydroxide is 500rfL
l ammonium phosphate aqueous solution (Po, 50■/l)
After stirring slowly for 1 hour and filtering, the PO4 concentration in the p solution was measured and found to be 3.71 ng/A.

このりん酸イオンを吸着した硫酸根含有水酸化アルミニ
ウムをHC7でpH4,3に調整した0、IN硫酸ナト
リウム水溶液200m1に入れゆっくり30分攪拌した
後濾過、水洗し、これを再び500rrLlのリン酸ア
ンモニウム溶液(50■/1PO4)に加えて吸着させ
、濾過水中の残留P04を測定した結果10.2■/l
であった。
This sulfate group-containing aluminum hydroxide that has adsorbed phosphate ions is added to 200ml of 0.IN sodium sulfate aqueous solution adjusted to pH 4.3 with HC7, stirred slowly for 30 minutes, filtered and washed with water, and then mixed with 500rrLl of ammonium phosphate again. The result of measuring the residual P04 in the filtered water by adding it to the solution (50■/1PO4) and adsorbing it was 10.2■/l.
Met.

一方比較例として0.IN硫酸すI−IJウム水溶液で
処理せずに同様にくり返し吸着試験をおこなった結果、
第1回泥液中のPO4は3.7■/l、再使用時のp液
中のPO4は45.8■/lであった。
On the other hand, as a comparative example, 0. As a result of repeated adsorption tests in the same manner without treatment with IN sulfuric acid I-IJ aqueous solution,
The PO4 in the first mud solution was 3.7 .mu./l, and the PO4 in the p solution at the time of reuse was 45.8 .mu./l.

実施例 2 100メツシユパスのNa型ゼオライト粉末5(Bi’
をA12032係濃度の硫酸アルミニウム水溶液125
rILlに分散させ攪拌しながら20係濃度の炭酸ナト
リウム水溶液をpHが6.3になるまで滴下した後、濾
過し、105℃で乾燥してゼオライトを硫酸根含有水酸
化アルミニウムで被覆した複合吸着剤を製造した。
Example 2 Na-type zeolite powder 5 (Bi'
A12032 aluminum sulfate aqueous solution 125
Composite adsorbent in which zeolite is coated with aluminum hydroxide containing sulfate radicals by dispersing it in rILl and dropping an aqueous solution of sodium carbonate at a concentration of 20 with stirring until the pH reaches 6.3, filtering and drying at 105°C. was manufactured.

本吸着剤1gを、NH423,Omty/ l 1P0
.9.7 mfil/l含む試水500m7に添加し、
30 rpm120°CI時間の条件で吸着させた後、
濾過し、泥液中のNH,、PO4を分析したところ、そ
れぞれ4.0〜/l、0.06〜/lであった。
1g of this adsorbent, NH423, Omty/l 1P0
.. Added to 500 m7 of sample water containing 9.7 mfil/l,
After adsorption under the conditions of 30 rpm 120° CI time,
When filtered and analyzed for NH, and PO4 in the slurry, they were 4.0~/l and 0.06~/l, respectively.

濾紙上の吸着剤をpH3,7のO,i N Na 2
SO爲生溶液でビーカーに洗い流し、同液を加えて全容
200rrLlとし、30 rpml 20℃0.5時
間の条件で再生した。
The adsorbent on the filter paper was treated with O, i N Na 2 at pH 3.7.
The beaker was rinsed with SO regeneration solution, the same solution was added to make a total volume of 200 rrLl, and the mixture was regenerated at 30 rpm at 20° C. for 0.5 hour.

再生後再び濾過、水洗し、上記試水でこれをビーカーに
洗い流し更に、試水を加えて全容500rnlとして、
再生第1回目の吸着試験を同様におこないp過水を分析
した結果NH44,2■/l。
After regeneration, filter again, wash with water, rinse it into a beaker with the above sample water, and add sample water to make a total volume of 500 rnl.
The adsorption test for the first regeneration was conducted in the same manner and the p-peroxide was analyzed and the result was NH44.2/l.

PO40,17〜/lであった。PO40.17~/l.

同様に再生をくりかえし、再生第2回目の吸着試験後の
濾過水中のNH4,PO,濃度はそれぞれ5.0〜/1
1.L87my/12であった。
The regeneration was repeated in the same way, and the concentrations of NH4 and PO in the filtered water after the second regeneration adsorption test were 5.0 to 1/1, respectively.
1. L was 87my/12.

一方再生をおこなわず同様な条件でくり返し吸着試験を
おこなった結果、第1回目濾過水中のNH,は4.0〜
/l 、 PO4は0.06〜/11第2回目濾過水中
(7)NH4は8.21n9/11PO4は1.72m
9/13.第3回目濾過水中のNH4は16.2mg、
#1PO4ハフ、6mg/lであった。
On the other hand, as a result of repeated adsorption tests under the same conditions without regeneration, the NH in the first filtered water was 4.0~
/l, PO4 is 0.06~/11 Second filtered water (7) NH4 is 8.21n9/11 PO4 is 1.72m
9/13. NH4 in the third filtered water is 16.2 mg,
#1 PO4 huff was 6 mg/l.

実施例 3 硫液アルミニウム水溶液(A12031.5%)5Kg
に尿素200gを溶解した後、沸点まで加熱し、5時間
攪拌をおこない、生成した沈澱物を濾過、水洗、乾燥し
て球状の粒子からなる硫酸根含有水酸化アルミニウム(
AA20340.3係、 5O418,3係)を得た。
Example 3 Sulfuric aluminum aqueous solution (A12031.5%) 5Kg
After dissolving 200 g of urea in the solution, it was heated to the boiling point and stirred for 5 hours. The resulting precipitate was filtered, washed with water, and dried to obtain sulfate-containing aluminum hydroxide (
AA20340.3, 5O418, 3) were obtained.

本吸着剤各1gを、KH2PO4;P水道水に溶解させ
てえた試水(Po、 52.4〜#) 500dに加え
て、20℃、1 hr130 rpmの条件下に吸着さ
せた後、沢過し、沢過水中のPO,を分析した。
In addition to 500 d of sample water (Po, 52.4~#) obtained by dissolving 1 g of each of these adsorbents in KH2PO4; Then, PO in the swamp water was analyzed.

沢紙上の吸着剤は、硫酸で所定pHに調整した5%Na
2SO4水溶液でビーカーに洗い流して全容200m1
とし、20℃、0.5 hr 30 vpmの条件で再
生した後、渥過水洗して、沖紙上の吸着剤を上記PO4
含有試水でビーカーに洗い流し、試水を加えて500m
1として再生第1回目の吸着試験をおこなった。
The adsorbent on the paper is 5% Na adjusted to a specified pH with sulfuric acid.
Rinse into a beaker with 2SO4 aqueous solution, total volume 200ml
After regenerating at 20°C and 0.5 hr 30 vpm, the adsorbent on the Oki paper was washed with water and the above PO4
Rinse into a beaker with containing sample water, add sample water and wait 500 m.
1, the first regeneration adsorption test was conducted.

同様に再生−吸着をくり返して、再生用 Na2SO4液のpHの再生効果におよぼす影響を調べ
た結果を表−3に示す。
The regeneration-adsorption process was repeated in the same manner, and the influence of the pH of the regeneration Na2SO4 liquid on the regeneration effect was investigated. The results are shown in Table 3.

実施例 4 内径25mm高さ300mmのガラス円筒に8〜20メ
ツシユのNa型ゼオライト50gを充填し、その上部に
実施例3で得た硫酸根含有水酸化アルミニウム5gを充
填した。
Example 4 A glass cylinder with an inner diameter of 25 mm and a height of 300 mm was filled with 50 g of 8 to 20 meshes of Na-type zeolite, and 5 g of the sulfate group-containing aluminum hydroxide obtained in Example 3 was filled above the cylinder.

この吸着カラムに上部より、下水の活性汚泥処理水(N
H48〜12m9/11平均10.37V/71P0.
4.1〜6.7m9/!3平均5.2〜.#)ヲsv2
.5で通水して処理水のNH,、PO,を一定時間毎に
測定し、処理水のNH4濃度が2.0 タ/ 7になっ
た時点の吸着剤1g当りの吸着量を測定した結果NH4
4,45In9であった。
Activated sludge treated sewage water (N
H48~12m9/11 average 10.37V/71P0.
4.1~6.7m9/! 3 average 5.2~. #) wosv2
.. 5, the NH, PO, of the treated water was measured at regular intervals, and the amount of adsorption per gram of adsorbent was measured when the NH4 concentration of the treated water reached 2.0 ta/7. NH4
It was 4,45In9.

また、この時点での処理水中のPO4は0.45m9/
Aであった。
Additionally, the PO4 in the treated water at this point was 0.45m9/
It was A.

次にpH3,5に調整した5%N a 2 S 04水
溶液11をSV2.5で通液した後水道水で洗い、再び
同試水を通水して吸着させ処理水のNH,濃度が2.0
〜/lになった時点での吸着剤1g当りの吸着量を測定
した結果4.52■であった。
Next, a 5% Na 2 S 04 aqueous solution 11 adjusted to pH 3.5 was passed through it at SV 2.5, washed with tap water, and the same sample water was passed through it again to adsorb it, so that the NH concentration of the treated water was 2. .0
The amount of adsorption per 1 g of adsorbent was measured at the time when the amount reached ~/l, and the result was 4.52 .

またこの時点での処理水中のPO4濃度は1.21n9
/lであった。
Also, the PO4 concentration in the treated water at this point was 1.21n9
/l.

Claims (1)

【特許請求の範囲】[Claims] l 、pH3〜5の硫酸すl−IJウム水溶液を用い
て、りん酸イオンを吸着した硫酸根含有水酸化アルミニ
ウムからなる吸着剤を再生する方法。
A method of regenerating an adsorbent made of aluminum hydroxide containing a sulfate group that has adsorbed phosphate ions using an aqueous solution of sulfuric acid and sodium sulfate having a pH of 3 to 5.
JP17191081A 1981-10-26 1981-10-26 How to regenerate adsorbent Expired JPS5944895B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP17191081A JPS5944895B2 (en) 1981-10-26 1981-10-26 How to regenerate adsorbent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP17191081A JPS5944895B2 (en) 1981-10-26 1981-10-26 How to regenerate adsorbent

Publications (2)

Publication Number Publication Date
JPS5874139A JPS5874139A (en) 1983-05-04
JPS5944895B2 true JPS5944895B2 (en) 1984-11-01

Family

ID=15932086

Family Applications (1)

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JP17191081A Expired JPS5944895B2 (en) 1981-10-26 1981-10-26 How to regenerate adsorbent

Country Status (1)

Country Link
JP (1) JPS5944895B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS60184992U (en) * 1984-05-18 1985-12-07 新日軽株式会社 Grids for windows, etc.

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS60184992U (en) * 1984-05-18 1985-12-07 新日軽株式会社 Grids for windows, etc.

Also Published As

Publication number Publication date
JPS5874139A (en) 1983-05-04

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