JP2000000404A - Titanium-containing flocculant for water treatment - Google Patents
Titanium-containing flocculant for water treatmentInfo
- Publication number
- JP2000000404A JP2000000404A JP18558698A JP18558698A JP2000000404A JP 2000000404 A JP2000000404 A JP 2000000404A JP 18558698 A JP18558698 A JP 18558698A JP 18558698 A JP18558698 A JP 18558698A JP 2000000404 A JP2000000404 A JP 2000000404A
- Authority
- JP
- Japan
- Prior art keywords
- hydrochloric acid
- titanium oxide
- water
- flocculant
- tio
- 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
Links
Landscapes
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、水処理用凝集剤、
特に上水道原水の浄化のための凝集剤に関する。The present invention relates to a coagulant for water treatment,
In particular, the present invention relates to a flocculant for purification of tap water.
【0002】[0002]
【従来の技術】現在、塩化アルミニウム、硫酸アルミニ
ウムなどのアルミ系凝集剤および塩化鉄、硫酸鉄などの
鉄系凝集剤が浄水処理、廃水処理などに使用されてい
る。また四塩化チタン[TiCl4 ]、チタニルクロラ
イド[TiOCl2 ],硫酸チタン[Ti(S
O4 )2 ]、チタニルサルフェート、[TiO(S
O4 )]などが水処理用凝集剤として利用可能なことは
よく知られている。(特開昭59−49811号公報、
特開平9−168786号公報、特開平9−23937
3号公報、特開平10−137508号公報)2. Description of the Related Art At present, aluminum-based coagulants such as aluminum chloride and aluminum sulfate and iron-based coagulants such as iron chloride and iron sulfate are used for water purification treatment and wastewater treatment. Further, titanium tetrachloride [TiCl 4 ], titanyl chloride [TiOCl 2 ], titanium sulfate [Ti (S
O 4 ) 2 ], titanyl sulfate, [TiO (S
It is well known that O 4 )] can be used as a coagulant for water treatment. (JP-A-59-49811,
JP-A-9-168786 and JP-A-9-23937
No. 3, JP-A-10-137508)
【0003】[0003]
【発明が解決しようとする課題】アルミ系凝集剤はアル
ミニウムとアルツハイマ型痴呆症との因果関係が懸念さ
れており、厚生省も注目している。鉄系凝集剤は鉄成分
による着色のために洗濯などには不適当である。また、
チタン酸系凝集剤の場合にはpHが中性領域での凝集能
が十分でないために、多量の助剤を併用する必要があり
工業的な利用にはさらなる改良が求められている。従っ
て、これらの代替物としてより安全で、かつ、高性能の
新しい凝集剤が求められている。The causal relationship between aluminum and Alzheimer's dementia has been concerned about aluminum-based coagulants, and the Ministry of Health has been paying attention. Iron-based flocculants are unsuitable for washing and the like due to coloring by iron components. Also,
In the case of titanic acid-based flocculants, the flocculation ability in the neutral pH range is not sufficient, so that it is necessary to use a large amount of an auxiliary agent, and further improvement is required for industrial use. Accordingly, there is a need for safer and higher performance new flocculants as substitutes for these.
【0004】[0004]
【発明を解決するための手段】本発明者らは、金属種と
して安全性が高く、着色の問題もないチタニウムを選定
し、各種のチタン化合物とその凝集能との関係を鋭意研
究した。その結果、硫酸チタンを出発原料として特殊な
処理を施して生成させた酸化チタン系コロイド粒子が、
新規な水処理用凝集剤として優れた性能を示すことを見
出し、本発明に到達した。Means for Solving the Problems The present inventors have selected titanium having high safety and no problem of coloring as a metal species, and have intensively studied the relationship between various titanium compounds and their cohesive ability. As a result, titanium oxide-based colloidal particles generated by performing a special treatment using titanium sulfate as a starting material,
The present inventors have found that they exhibit excellent performance as a novel coagulant for water treatment, and have reached the present invention.
【0005】すなわち、出発原料として硫酸チタン(T
iO2 分:10〜30wt%、H2 SO4 分:15〜45
wt%)を用い、5〜20wt%水酸化ナトリウムによって
pH3〜8の範囲に中和して生成する析出物をTiO2
に対して20〜45wt%の塩酸で解膠した後60〜95
℃において30〜120分間熟成することによって得ら
れる粒子径20〜70nmの酸化チタン系コロイド粒子
が、前記の課題を解決するための水処理用凝集剤となり
うることを確認した。この酸化チタン系コロイド粒子は
オルトチタン酸であることがX線回折の測定によって確
認された。最適な凝集能を示す酸化チタン系コロイド粒
子の生成条件ならびに特性は、次の通りであることを確
認した。That is, titanium sulfate (T
iO 2 min: 10 to 30 wt%, H 2 SO 4 min: 15 to 45
wt%) and neutralized with 5-20 wt% sodium hydroxide to a pH in the range of 3 to 8 to form a precipitate formed of TiO 2
60-95% after peptization with 20-45 wt% hydrochloric acid
It was confirmed that titanium oxide-based colloidal particles having a particle diameter of 20 to 70 nm obtained by aging at 30 ° C for 30 to 120 minutes can be used as a coagulant for water treatment to solve the above-mentioned problems. The titanium oxide colloid particles were confirmed to be orthotitanic acid by X-ray diffraction measurement. It was confirmed that the production conditions and characteristics of the titanium oxide-based colloid particles exhibiting the optimum aggregating ability were as follows.
【0006】 表1 最適コロイド粒子の生成条件と特性 ───────────────────────────────── 硫酸チタンの中和時のpH値: 3. 5〜7. 0 解膠時の熟成塩酸濃度 : 35〜45wt%(対TiO2) 熟 成 時 間 : 40〜60分間 熟 成 温 度 : 70〜90℃ ζ−電 位 : −10 〜 +10mV 平 均 粒 子 径 : 30〜50nm 粒度分布 : 30nm以下 2. 0wt% 30〜40nm 48. 0wt% 40〜50nm 47. 6wt% 50nm以上 2. 4wt% ─────────────────────────────────Table 1 Conditions and characteristics of optimum colloidal particles の 中 In titanium sulfate PH value at the time of summation: 3.5-7.0 Aging hydrochloric acid concentration during peptization: 35-45 wt% (vs. TiO 2 ) Aging time: 40-60 minutes Aging temperature: 70-90 ° C. Potential: -10 to +10 mV Average particle size: 30 to 50 nm Particle size distribution: 30 nm or less 2.0 wt% 30 to 40 nm 48.0 wt% 40 to 50 nm 47.6 wt% 50 nm or more 2.4 wt% ────────────────────────────
【0007】本発明の酸化チタン系凝集剤の使用量は、
通常、上水用原水に対してTiO2として2〜5pp
m、好ましくは3ppmの添加で十分であり、添加方法
は特に限定されない。本凝集剤の効果を高めるために
は、浄水に添加する時の攪拌が強力なほど好ましく、循
環ポンプの入口側の送水管の途中で注入するなどの工夫
により凝集能が向上する。本発明のコロイド状水和酸化
チタンの淀川水系の原水に対する凝集能は、硫酸バンド
より優れており、アルミ系凝集剤と同等かそれ以上の凝
集能を有することが明らかとなった。The amount of the titanium oxide-based coagulant of the present invention is as follows:
Usually, 2 to 5 pp as TiO2 to raw water for drinking water
m, preferably 3 ppm, is sufficient, and the method of addition is not particularly limited. In order to enhance the effect of the coagulant, the stirring at the time of adding it to the purified water is preferably as strong as possible, and the coagulation ability is improved by a device such as injection in the middle of a water pipe on the inlet side of the circulation pump. The aggregating ability of the colloidal hydrated titanium oxide of the present invention in raw water of the Yodogawa water system was superior to the sulfate band, and was found to have the same or better aggregating ability as the aluminum-based flocculant.
【0008】なお、本発明のチタン系凝集剤の安全性デ
ータは次の通りであり、安全性が高く、また着色の問題
もない。 LD50 : 3.321g/kg(ラット) Amesテスト: 陰性 発 ガ ン 性: Table−3にリストアップ(W
HO)[0008] The safety data of the titanium-based flocculant of the present invention are as follows, and the safety is high and there is no problem of coloring. LD 50 : 3.321 g / kg (rat) Ames test: negative Carcinogenicity: Listed in Table-3 (W
HO)
【0009】[0009]
【発明の実施の形態】以下、本発明を典型的な実施例に
よりさらに詳細に説明するが、後述する実施例により本
発明が限定されることを意図するものではない。BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be described in more detail with reference to typical examples, but it is not intended that the present invention be limited by the examples described below.
【0010】 表2 凝集試験法 ─────────────────────────────────── 原水の種類: 水簸カオリン(関東化学社製)/水道水 濁 度 :29. 3度 pH :7. 2 アルカリ度:30mg/L 原水量 : 500mL 試験器 : ジャーテスタ(宮本理研社製JMD−8) 攪拌条件 : 急速攪拌 110rpm、10分間 緩速攪拌 40rpm、10分間 静 置 10分間 濁度計 : 三菱化成工業社製SEP−PT−501D 評 価 : フロック沈降性 ○:良 △:並 ×:不良 ───────────────────────────────────[0010] Table 2 Coagulation test method ─────────────────────────────────── Type of raw water: Elutriated kaolin (Kanto Chemical Co., Ltd.) / Tap water Turbidity: 29.3 degrees pH: 7.2 Alkalinity: 30 mg / L Raw water amount: 500 mL Tester: Jar tester (Miyamoto Riken Co., Ltd. JMD-8) Stirring conditions: Rapid stirring 110 rpm, 10 minutes Slow stirring 40 rpm, 10 minutes Stand still 10 minutes Turbidimeter: SEP-PT-501D manufactured by Mitsubishi Kasei Kogyo Evaluation: Flock sedimentation ○: Good △: Average ×: Poor ─────────────────────────────
【0011】比較対象用凝集剤: ・硫酸アルミニウム(大明化学工業株式会社製) ・チタニヤゾル(テイカ株式会社製) テイカ社製硫酸チタンを105℃において熱加水分解し
た後、硫酸分を48wt%水酸化ナトリウムで中和し、水
洗後、35wt%塩酸で解膠したオルトチタン酸の10wt
%ゾル ・CRシード(テイカ株式会社製) テイカ社製硫酸チタンを105℃において熱加水分解し
た後、生成したオルソチタン酸を48wt%水酸化ナトリ
ウムと混合し、100℃に加熱して非晶質(無定形)に
する。水洗後、35wt%塩酸で解膠した製品 ・本発明凝集剤(実施例1、テイカ社/大明化学社共同
開発製品) 硫酸チタンを用いて中和後、pH:4.0、解膠時の塩
酸濃度:35wt%、温度:80℃で生成したコロイド状
水和酸化チタンCoagulants for comparison: Aluminum sulfate (manufactured by Daimei Chemical Co., Ltd.) Titanium sol (manufactured by Teica Co., Ltd.) Titanium sulfate manufactured by Teika Co., Ltd. is thermally hydrolyzed at 105 ° C., and then the sulfuric acid content is 48 wt% hydroxylated. Neutralized with sodium, washed with water, 10 wt% of orthotitanic acid peptized with 35 wt% hydrochloric acid
% Sol CR seed (manufactured by Teica Co., Ltd.) Titanium sulfate manufactured by Teika Co. is thermally hydrolyzed at 105 ° C., and the resulting orthotitanic acid is mixed with 48 wt% sodium hydroxide and heated to 100 ° C. to form an amorphous material. (Amorphous). Product washed with water and peptized with 35 wt% hydrochloric acid ・ Coagulant of the present invention (Example 1, a product jointly developed by Teica and Daimei Chemical Co.) After neutralization with titanium sulfate, pH: 4.0 Hydrochloric acid concentration: 35 wt%, Colloidal hydrated titanium oxide formed at a temperature of 80 ° C
【0012】実施例1 加水分解pH値と凝集能との関係 櫂型攪拌機付50L琺瑯ビーカーに常温で12wt%水酸
化ナトリウム(ρ=1.13)、9Lを投入し、引き続
き硫酸チタン(テイカ社製 TiO2 :250g /L、
全H2 SO4 :400g /L)、10Lを攪拌しながら
添加する。添加終了後、直ちにpH値を48wt%水酸化
ナトリウムまたは98wt%硫酸で表3の値へ調整し、さ
らに30分間、70℃において加熱した後、濾過水洗し
て水和酸化チタンを得る。洗浄水量はケーキの2倍量と
し硫酸根含有量は2%wt以下とする。解膠は、TiO2
濃度が5wt%となるように水, 475mLを添加して調
整し、TiO2 に対して35wt%となるように35%塩
酸、25mLを添加した後、85℃において40分間処
理した。Example 1 Relationship between hydrolysis pH value and coagulation ability In a 50 L enamel beaker equipped with a paddle-type stirrer, 9 L of 12 wt% sodium hydroxide (ρ = 1.13) was added at room temperature, and then titanium sulfate (Taika Co., Ltd.) TiO 2 : 250 g / L,
(Total H 2 SO 4 : 400 g / L), 10 L are added with stirring. Immediately after completion of the addition, the pH value is adjusted to the value shown in Table 3 with 48 wt% sodium hydroxide or 98 wt% sulfuric acid, and the mixture is further heated at 70 ° C. for 30 minutes, and then washed with filtered water to obtain hydrated titanium oxide. The amount of washing water is twice as much as the cake, and the sulfate content is 2% wt or less. Peptization is TiO 2
Water and 475 mL were added to adjust the concentration to 5 wt%, and 35% hydrochloric acid and 25 mL to 35 wt% with respect to TiO 2 were added, followed by treatment at 85 ° C. for 40 minutes.
【0013】得られたコロイド溶液は、BROOKHA
VEN INSTRUMENT社製B1−90型PAR
TICLE SIZER粒度計を使用して粒度分布なら
びに平均粒子径を測定した。The obtained colloid solution is BROOKHA
VEN INSTRUMENT B1-90 PAR
The particle size distribution and the average particle size were measured using a TICLE Sizer particle sizer.
【0014】表3に凝集能実験結果を示す。 表3 加水分解pH値と凝集能との関係結果(添加量3ppm as TiO2 ) ────────────────────────────────── 試料 pH 平均粒子径 上澄濁度 沈降性 備考 (nm) (度) ────────────────────────────────── 1 2 <60nm − × 加水分解不良 2 3 〃 1. 0 △ 3 4 〃 0. 5 ○ 4 5 〃 0. 7 ○ 5 6 〃 0. 9 △ 6 7 〃 1. 0 △ 7 8 〃 2. 5 △ 8 9 〃 − × ──────────────────────────────────Table 3 shows the results of the agglutination test. Table 3 Results of relationship between hydrolysis pH value and aggregation ability (addition amount: 3 ppm as TiO 2 ) ───── Sample pH average particle size Supernatant turbidity Sedimentation Remarks (nm) (degree) ─────────────────────────── 1 12 <60 nm-× poor hydrolysis 23 〃 1.0 △ 34 △ 0.5 ○ 45 〃 0.7 ○ 56 〃 0.9 △ 67 7 1.0 △ 78 〃 2.5 △ 89 〃-× ──────────────────────────────────
【0015】表3から明らかなように本発明品の凝集能
は加水分解時のpH値が3〜8の範囲で上澄み濁度と沈
降性が優れている。pH2以下の場合は加水分解が不十
分であり、またpH9以上の場合は凝集能が低い。As is apparent from Table 3, the coagulation ability of the product of the present invention is excellent in supernatant turbidity and sedimentation when the pH value during hydrolysis is in the range of 3 to 8. When the pH is 2 or less, the hydrolysis is insufficient, and when the pH is 9 or more, the aggregation ability is low.
【0016】実施例2 解膠時の塩酸濃度および温度と凝集能との関係 攪拌機付1Lガラス製ビーカーを用いて実施例1の水和
酸化チタンケーキ、170gを水道水、475mLによ
りスラリー化し、さらに、濃塩酸を加えてTiO2 :5
wt%、およびTiO2 に対してHCl:15,25,3
5,45,55wt%の5サンプルを各0. 5L調製し
た。ガラス製三ッ口フラスコに移して昇温時間:60分
間、熟成時間:40分間、熟成温度:70、80、90
℃において解膠した。Example 2 Relationship between Hydrochloric Acid Concentration and Temperature during Peptization and Coagulation Ability A 170 g hydrated titanium oxide cake of Example 1 was slurried with 475 mL of tap water using a 1 L glass beaker equipped with a stirrer. , Concentrated hydrochloric acid and TiO 2 : 5
wt%, and HCl based on TiO 2 : 15,25,3
Five samples of 5, 45, 55 wt% were prepared in 0.5 L each. Transfer to a glass three-necked flask and heat up: 60 minutes, aging time: 40 minutes, aging temperature: 70, 80, 90
Peptized at 0 ° C.
【0017】表 に実験結果を示す。 表4 解膠時の塩酸濃度および温度と凝集能との関係 (添加量 3ppm as TiO2 ) ──────────────────────────────── 熟成温度 70℃ 80℃ 90℃ 塩酸濃度 凝 集 能 (wt% to TiO2 )上澄濁度 沈降性 上澄濁度 沈降性 上澄濁度 沈降性 15 9. 0 × 7. 0 × 5. 0 × 25 3. 5 △ 3. 0 △ 2. 0 △ 35 1. 0 ○ 0. 5 〇 1. 3 〇 45 0. 8 ○ 0. 7 〇 3. 0 △ 55 7. 0 × 6. 5 × 9. 2 × ─────────────────────────────────Table 1 shows the experimental results. Table 4 Relationship between hydrochloric acid concentration and temperature during peptization and coagulation ability (addition amount: 3 ppm as TiO 2 ) ────────────────────────── ────── Aging temperature 70 ° C 80 ° C 90 ° C Hydrochloric acid concentration Aggregation ability (wt% to TiO 2 ) Superficial turbidity Precipitating Superficial turbidity Precipitating Superficial turbidity Precipitating 159.0 × 7 0 × 5.0 × 25 3.5 △ 3.0 △ 2.0 2351.0 1.0〇0.5〇1.3〇450.8 0.8 ○ 0.7〇3.0 △ 55 △ 7.0 × 6.5 × 9.2 × ─────────────────────────────────
【0018】最適凝集能を発現する熟成温度と塩酸濃度
は、それぞれ:70〜90℃、35〜45wt%であっ
た。The ripening temperature and the hydrochloric acid concentration at which the optimum flocculating ability was developed were respectively 70 to 90 ° C. and 35 to 45 wt%.
【0019】実施例3 熟成後塩酸添加量と凝集能との関係 攪拌機付1Lガラス製ビーカーで実施例1の水和酸化チ
タンケーキ、170gを水道水、475mLを用いてス
ラリー化し、さらに濃塩酸を加えてTiO2 :5wt%お
よびTiO2 に対してHCl:35wt%に調整した。ガ
ラス製三ッ口フラスコに移して60分間で80℃に昇温
し、この温度において40分間熟成して解膠した。この
解膠したスラリーに濃塩酸をTiO2 に対してそれぞれ
0、50、100、150、200、250,300wt
%添加した。Example 3 Relationship between the amount of added hydrochloric acid and the coagulation ability after aging 170 g of the hydrated titanium oxide cake of Example 1 was slurried with 475 mL of tap water using a 1 L glass beaker equipped with a stirrer. In addition, TiO 2 was adjusted to 5 wt% and HCl to 35 wt% with respect to TiO 2 . The mixture was transferred to a glass three-necked flask, heated to 80 ° C. for 60 minutes, aged at this temperature for 40 minutes, and peptized. Each of concentrated hydrochloric acid to the peptized slurry against TiO 2 0,50,100,150,200,250,300wt
% Was added.
【0020】 表5 熟成後塩酸添加量と凝集能との関係 (添加量3ppm as TiO2) ─────────────────────────────── 塩酸添加量 粒子径 凝 集 能 (wt. %対TiO2) (nm) 上澄濁度(度) 沈降性 ─────────────────────────────── 0 1. 0 ○ 50 0. 4 ○ 100 0. 8 ○ 150 0. 7 ○ 200 1. 0 ○ 250 27 × 300 28 × ────────────────────────────── 解膠スラリーに塩酸を0〜200wt%添加することによ
り凝集能が向上する。Table 5 Relationship between the amount of hydrochloric acid added after aging and the coagulation ability (3 ppm as TiO 2 added)量 Amount of hydrochloric acid added Particle size Aggregation ability (wt.% Vs. TiO 2 ) (nm) Supernatant turbidity (degree) Precipitation ───────────────── ────────────── 0 1.0 ○ 50 0.4 ○ 100 0.8 150 150 0.7 200 200 1.0 ○ 250 27 × 300 28 × ─────凝集 Addition of 0 to 200 wt% of hydrochloric acid to the deflocculated slurry improves the coagulation ability.
【0021】実施例4 淀川原水に対する凝集能 コロイド状水和酸化チタンの製法条件 水和酸化チタン製造条件: 実施例1と同じ 中和pH : 4. 0 解膠条件 : 実施例2,実施例3と同じ 熟成時塩酸濃度: 35wt% 温 度 : 80℃ 塩酸添加量 : 0wt%、50wt%Example 4 Agglomeration ability to Yodogawa raw water Conditions for producing colloidal hydrated titanium oxide Production conditions for hydrated titanium oxide: Same as in Example 1 Neutralization pH: 4.0 Peptization conditions: Examples 2 and 3 Same as above Concentration of hydrochloric acid during aging: 35 wt% Temperature: 80 ° C Hydrochloric acid addition amount: 0 wt%, 50 wt%
【0022】 表6 淀川原水に対する凝集能 添加量(as TiO2 ) ────────────────────────────────── 凝集剤 3ppm 5ppm ───────────────────── 上澄濁度 沈降性 上澄濁度 沈降性 ────────────────────────────────── コロイド状水和酸化チタン 0. 3 ○ 0. 3 ○ 塩酸添加量= 0wt% コロイド状水和酸化チタン 0. 4 ○ 0. 3 ○ 塩酸添加量=50wt% 硫酸アルミニウム 0. 4 ○ 1. 2 △ ────────────────────────────────── コロイド状水和酸化チタンは性能的にも経済的にも無機
系凝集剤として多量に使用されている硫酸アルミニウム
の代替品となりうる。Table 6 Aggregation ability for Yodogawa raw water Addition amount (as TiO 2 ) ─ flocculant 3ppm 5ppm ───────────────────── supernatant turbidity sedimentation supernatant turbidity sedimentation ────────────水 和 Colloidal hydrated titanium oxide 0.3 ○ 0.3 ○ Hydrochloric acid addition amount = 0 wt% Colloidal hydrated titanium oxide 0.3% 4 ○ 0.3 ○ Amount of hydrochloric acid added = 50wt% Aluminum sulfate 0.4 ○ 1.2 △ ────────────────────────────水 和 Colloidal hydrated titanium oxide can replace aluminum sulfate, which is used in large quantities as an inorganic coagulant, both in terms of performance and economy.
【0023】実施例5 処理工程別粒度と凝集能との関係 試料:各工程のコロイド状水和酸化チタンを上水でTi
O2 =0. 15wt%に調製 粒度分布測定器:BROOKHAVEN INSTRUMENT 社製B 1−9
0 PARTICLE SIZER 処理工程別コロイド状水和酸化チタ
ンのζ−電位の測定 原水量:500m L 凝集剤添加量:10ppm (as TiO2 ) 測定器:レ−ザ−ゼ−タ−電位計(大塚電子社製LEZA
型) 表7 処理工程別粒度、ζ−電位と凝集能との関係 (添加量3ppm as TiO2) ────────────────────────────────── 工程別試料 粒度 ζ−電位 濁度 沈降性 (nm) (mV) (度) ────────────────────────────────── ケーキ+水 233 −19. 10 30 × ケーキ+水+35wt%塩酸 248 6 △ 解膠熟成液 54 0. 8 ○ 解膠熟成液+150wt%塩酸 43 +11. 72 0. 5 ○ 解膠熟成液+200wt%塩酸 30 0. 6 ○ チタニアゾル 64 −3. 95 20 × CRシード 58 −3. 96 20 × ────────────────────────────────── 硫酸チタニル 400〜700 >30 × ────────────────────────────────── 塩酸処理によってコロイド粒子は見かけ粒度が小さくな
る。また、コロイド状水和酸化チタンの塩酸添加物は原
水中で+電位になる。Example 5 Relationship between Particle Size and Aggregation Ability in Each Treatment Process Sample: Colloidal hydrated titanium oxide in each process was washed with clean water using Ti
O 2 = 0.15 wt% adjusted Particle size distribution analyzer: B1-9 manufactured by BROOKHAVEN INSTRUMENT
0 PARTICLE SIZER Measurement of ζ-potential of colloidal hydrated titanium oxide for each treatment step Raw water amount: 500 mL Coagulant addition amount: 10 ppm (as TiO 2 ) Measuring instrument: laser-zeta-electrometer (Otsuka Electronics) LEZA
Type) Table 7 Relationship between particle size, ζ-potential and coagulation ability by treatment process (addition amount 3ppm as TiO 2 ) ────────────────────────試 料 Sample size by process ζ-potential turbidity sedimentation (nm) (mV) (degree) ──────────────────── ────────────── Cake + water 233-19.10 30 × cake + water + 35 wt% hydrochloric acid 248.6 △ peptizing ripening solution 54 0.8 ○ peptizing ripening solution + 150 wt% hydrochloric acid 43 +11.720.5 ○ Peptizing ripening solution + 200wt% hydrochloric acid 300.6 ○ Titania sol 64-3.95 20 × CR seed 58-3.96 20 × ──────────────チ Titanyl sulfate 400-700> 30 × ────────────────────── ──コ ロ イ ド The apparent particle size of the colloid particles is reduced by the hydrochloric acid treatment. Further, the hydrochloric acid additive of the colloidal hydrated titanium oxide has a positive potential in raw water.
【0024】実施例6 表8 原水の攪拌条件と凝集能との関係 ──────────────────────────── 攪拌条件 回転数(ppm ) 回転時間(分) ──────────────────────────── 1 急速攪拌 110 10 2 〃 180 5 3 〃 180 10 緩速攪拌 40 10 静 置 − 10 ────────────────────────────Example 6 Table 8 Relationship between Raw Water Stirring Conditions and Aggregation Ability Stirring Conditions Rotational Speed (Ppm) Rotation time (min) ──────────────────────────── 1 Rapid stirring 110 10 2 〃 180 53 3 180 180 10 Slow Rapid stirring 40 10 Static -10 ────────────────────────────
【0025】上記の攪拌条件と凝集能について試験して
表9の結果を得た。 表9 凝集能実験結果 (添加量=3ppm as TiO2 ) ──────────────────────── 攪拌条件 濁度(度) 沈降性 ──────────────────────── 1 1. 4 △ 2 1. 2 △ 3 0. 4 ○ ──────────────────────── 急速攪拌の回転数が増し、撹拌時間が長くなるに従い凝
集能がアップする。The above stirring conditions and aggregating ability were tested to obtain the results shown in Table 9. Table 9 Results of agglutination test (addition amount = 3ppm as TiO 2 ) ──────────────────────── Stirring conditions Turbidity (degree) Precipitation ── ────────────────────── 1 1.4 △ 2 1.2 △ 3 0.4 ○ ○回 転 The number of revolutions of rapid stirring increases, and the aggregating ability increases as the stirring time increases.
───────────────────────────────────────────────────── フロントページの続き (72)発明者 岩根 信雄 大阪府大阪市中央区博労町3丁目6番1号 テイカ株式会社内 (72)発明者 藤沢 英昭 長野県上伊那郡南箕輪村3685番地の2 大 明化学工業株式会社内 (72)発明者 田中 美太郎 兵庫県西宮市上甲東園4丁目7番30号 Fターム(参考) 4D015 BA03 BA08 BA10 CA14 DA30 DC03 EA04 EA32 EA35 4D062 BA03 BA08 BA10 CA14 DA30 DC03 EA04 EA32 EA35 ──────────────────────────────────────────────────続 き Continued on the front page (72) Inventor Nobuo Iwane 3-6-1, Hiroruro-cho, Chuo-ku, Osaka-shi, Osaka Inside Teika Co., Ltd. (72) Inventor Hideaki Fujisawa 3585 No. 385 Minamiminowa-mura, Kamiina-gun, Nagano Prefecture Within Chemical Industry Co., Ltd. (72) Inventor Mitaro Tanaka 4- 7-30 Joko Higashi-en, Nishinomiya-shi, Hyogo F-term (reference) 4D015 BA03 BA08 BA10 CA14 DA30 DC03 EA04 EA32 EA35 4D062 BA03 BA08 BA10 CA14 DA30 DC03 EA04 EA32 EA35
Claims (3)
加水分解し、生成する水和酸化チタンの沈澱を塩酸によ
り解膠して得られる平均粒子径20〜70nmのコロイ
ドよりなる水処理用チタン系凝集剤。1. A titanium system for water treatment comprising a colloid having an average particle diameter of 20 to 70 nm obtained by hydrolyzing titanium sulfate in an aqueous solution at pH 3 to 8 and peptizing the resulting precipitate of hydrated titanium oxide with hydrochloric acid. Flocculant.
ムによりpH3〜8の範囲に調節する工程、 (b)この溶液を60〜80℃に加熱し水和酸化チタン
を沈澱させる工程、 (c)生成した水和酸化チタンの沈澱を回収し、硫酸根
を実質上含まなくなるまで水洗する工程、 (d)水洗した水和酸化チタンケーキを再び水に懸濁
し、懸濁液へHCl/TiO2 で表して20〜45wt
%の塩酸を添加する工程、 (e)塩酸を添加した懸濁液を60〜95℃において3
0〜120分間熟成する工程、 (f)場合によりHCl/TiO2 で表わして200w
t%までの塩酸をさらに添加する工程、 を含む請求項1の凝集剤の製造法。(A) a step of adjusting the pH of the aqueous solution of titanium sulfate to 3 to 8 with sodium hydroxide; (b) a step of heating the solution to 60 to 80 ° C. to precipitate hydrated titanium oxide; ) A step of collecting the formed precipitate of hydrated titanium oxide and washing with water until substantially free of sulfate groups; (d) suspending the washed hydrated titanium oxide cake in water again, and adding HCl / TiO 2 to the suspension. 20 to 45 wt
(E) adding the hydrochloric acid-added suspension to the suspension at 60 to 95 ° C. for 3 hours.
Aging for 0-120 minutes; (f) optionally 200 w, expressed as HCl / TiO 2
The process for producing a flocculant according to claim 1, further comprising the step of adding hydrochloric acid up to t%.
て2ppm以上を添加攪拌し、生成したフロックを上澄
みから分離することを特徴とする水特に上水道水の浄化
方法。3. A method for purifying water, particularly tap water, wherein the flocculant of claim 1 is added to raw water at 2 ppm or more as TiO 2 and stirred, and the generated floc is separated from the supernatant.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP18558698A JP2000000404A (en) | 1998-06-16 | 1998-06-16 | Titanium-containing flocculant for water treatment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP18558698A JP2000000404A (en) | 1998-06-16 | 1998-06-16 | Titanium-containing flocculant for water treatment |
Publications (1)
Publication Number | Publication Date |
---|---|
JP2000000404A true JP2000000404A (en) | 2000-01-07 |
Family
ID=16173405
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP18558698A Pending JP2000000404A (en) | 1998-06-16 | 1998-06-16 | Titanium-containing flocculant for water treatment |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2000000404A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104261529A (en) * | 2014-09-19 | 2015-01-07 | 句容亿格纳米材料厂 | Nano titanium dioxide coating flocculant and preparation method thereof |
CN115504555A (en) * | 2022-09-27 | 2022-12-23 | 齐鲁工业大学 | Coal gasification slag-based composite ferric aluminum silicate flocculant and preparation method and application thereof |
-
1998
- 1998-06-16 JP JP18558698A patent/JP2000000404A/en active Pending
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104261529A (en) * | 2014-09-19 | 2015-01-07 | 句容亿格纳米材料厂 | Nano titanium dioxide coating flocculant and preparation method thereof |
CN115504555A (en) * | 2022-09-27 | 2022-12-23 | 齐鲁工业大学 | Coal gasification slag-based composite ferric aluminum silicate flocculant and preparation method and application thereof |
CN115504555B (en) * | 2022-09-27 | 2023-09-26 | 齐鲁工业大学 | Coal gas slag-based composite ferric aluminum silicate flocculant and preparation method and application thereof |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
EP0444798B1 (en) | Method for the preparation of titanium dioxide | |
US3146119A (en) | Pigment treatment | |
JPH09165218A (en) | Nanodiffusivity titanium dioxide, its preparation and its use | |
TW492948B (en) | Flocculant compositions and water treatment method using the same | |
JP2009227519A (en) | Method for producing rutile-type titanium dioxide fine particles | |
JPH07315838A (en) | Titanium dioxide of durable pigment and its preparation | |
US4268422A (en) | Titanium dioxide hydrate of a particular structure and process of manufacture thereof | |
US8268203B2 (en) | Method for producing microcrystalline titanium oxide | |
JP2000000404A (en) | Titanium-containing flocculant for water treatment | |
US5792250A (en) | Process for the production of inorganically coated pigments and fillers | |
US2220966A (en) | Titanium oxide suspensions | |
CN109219577B (en) | Preparation of nanoparticulate titanium dioxide | |
JP3952122B2 (en) | Titanium-based flocculant | |
JP2000202207A (en) | Coagulant for water treatment and production thereof | |
US5656175A (en) | Recovery of metal oxides from a slurry | |
JP2002028404A (en) | Titanium based flocculating agent | |
JP3806790B2 (en) | Process for producing spindle-shaped titanium dioxide | |
JP2000308803A (en) | Flocculant for water treatment and its production and flocculating method for water | |
JP2002079003A (en) | Inorganic flocculant using highly purified ferric salt and manufacturing method thereof and processing apparatus in water-purification processing | |
JP4164721B2 (en) | Flocculant composition for water treatment and use thereof | |
JPH11188204A (en) | Titanium based flocculating agent for water treatment | |
US2479637A (en) | Titanium oxide pigment production | |
JP3694813B2 (en) | Flocculant for water treatment | |
US3459575A (en) | Titanium pigment manufacture | |
JP2000279708A (en) | Inorganic flocculating agent for water treatment and its production |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20041013 |
|
A711 | Notification of change in applicant |
Effective date: 20041013 Free format text: JAPANESE INTERMEDIATE CODE: A711 |
|
A521 | Written amendment |
Free format text: JAPANESE INTERMEDIATE CODE: A821 Effective date: 20041013 |
|
A977 | Report on retrieval |
Free format text: JAPANESE INTERMEDIATE CODE: A971007 Effective date: 20061012 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20061024 |
|
A131 | Notification of reasons for refusal |
Effective date: 20071211 Free format text: JAPANESE INTERMEDIATE CODE: A131 |
|
A02 | Decision of refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A02 Effective date: 20080408 |