JPS5948154B2 - Wastewater purification method - Google Patents
Wastewater purification methodInfo
- Publication number
- JPS5948154B2 JPS5948154B2 JP2131279A JP2131279A JPS5948154B2 JP S5948154 B2 JPS5948154 B2 JP S5948154B2 JP 2131279 A JP2131279 A JP 2131279A JP 2131279 A JP2131279 A JP 2131279A JP S5948154 B2 JPS5948154 B2 JP S5948154B2
- Authority
- JP
- Japan
- Prior art keywords
- wastewater
- silicic acid
- added
- water
- ppm
- 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
Links
Landscapes
- Water Treatment By Sorption (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Removal Of Specific Substances (AREA)
Description
【発明の詳細な説明】
この発明は、廃水の浄化処理方法、更に詳しくはけい酸
および金属塩を含有する油廃水の浄化処理方法に係るも
のである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for purifying wastewater, and more particularly to a method for purifying oily wastewater containing silicic acid and metal salts.
けい酸および金属塩を含有する油廃水は、自動車工業、
産業機械工業等の諸事業所の製造工程から排出されてい
る。Oil wastewater containing silicic acid and metal salts is used in the automotive industry,
Emitted from manufacturing processes at various establishments such as the industrial machinery industry.
これらの油廃水の浄化処理方法としては、これらの油廃
水がアルカリ性である為に、一般に鉱酸でpHを4〜5
に調整し、ついでエマルジョン分解剤を添加または添加
しないで凝集剤を添加し、更にアルカリ剤を添加してp
Hを8〜9とし、含有物を凝集沈澱せしめ、固液分離に
より浄化処理する方法が行われていた。As a purification treatment method for these oil wastewaters, since these oil wastewaters are alkaline, the pH is generally adjusted to 4 to 5 using mineral acid.
Then, add a flocculant with or without adding an emulsion decomposer, and then add an alkaline agent to
A method has been used in which H is set to 8 to 9, the contained substances are coagulated and precipitated, and the purification treatment is performed by solid-liquid separation.
しかしながらかかる従来法では、金属塩、特に亜鉛、お
よび油分とBOD、CODで表示される有機性汚染物質
の除去が十分でなく、処理効果が低い。However, such conventional methods do not sufficiently remove metal salts, especially zinc, and organic pollutants represented by oil and BOD and COD, resulting in low treatment effects.
この発明の目的は、けい酸および金属塩を含有する油廃
水から、金属、油およびBOD、CODで表示される有
機性汚染物質を効果的に除去する処理方法を提供するに
ある。An object of the present invention is to provide a treatment method for effectively removing metals, oil, and organic pollutants expressed as BOD and COD from oil wastewater containing silicic acid and metal salts.
この発明による廃水の浄化処理方法は、(、すい酸およ
び金属塩を含有する油廃水に、該廃水中のけい酸濃度が
約500ppm未満である場合には水溶性けい酸塩を添
加してけい酸濃度を約500ppm以上とした後水溶性
アルミニウム塩および消石灰を添加してpHを10〜1
2.5とし、生成した沈澱を除去した後、鉱酸を添加し
てpHを6〜8とし固形吸着剤と接触せしめることを特
徴とする廃水の浄化処理方法である。The method for purifying wastewater according to the present invention includes adding a water-soluble silicate to oil wastewater containing sulfuric acid and metal salts when the silicic acid concentration in the wastewater is less than about 500 ppm. After adjusting the acid concentration to about 500 ppm or more, water-soluble aluminum salt and slaked lime were added to adjust the pH to 10 to 1.
2.5, remove the generated precipitate, and then add mineral acid to adjust the pH to 6 to 8 and bring it into contact with a solid adsorbent.
この発明による方法の対象とされる油廃水に含まれるけ
い酸並びに金属塩の代表的なものは、イオン状および/
またはコロイド状のけい酸並びに亜鉛および/または鉄
の塩類である。Typical silicic acid and metal salts contained in oil wastewater, which are the targets of the method according to the present invention, are ionic and/or metal salts.
or colloidal silicic acid and zinc and/or iron salts.
この発明による廃水の浄化処理方法に使用される水溶性
けい酸塩として、けい酸ナトリウム、けい酸カリウム、
エチルシリケート等が挙げられるが、けい酸ナトリウム
が最も容易に入手することができ効果をあげることがで
きるので望ましい。The water-soluble silicates used in the wastewater purification method according to the present invention include sodium silicate, potassium silicate,
Examples include ethyl silicate, but sodium silicate is preferred because it is the most easily available and is most effective.
また本発明者等は廃水中の金属および油分と、BOD、
CODで表示される有機性汚染物質の凝集沈澱除去につ
いて種々検討を重ねた結果、廃水中のイオン状およびコ
ロイド状のけい酸の量が著しく影響することを見出した
。In addition, the present inventors have discovered that metals and oil in wastewater, BOD,
As a result of various studies on the coagulation and precipitation removal of organic pollutants expressed by COD, it was discovered that the amount of ionic and colloidal silicic acid in wastewater has a significant effect.
即ち廃水中のけい酸濃度が約500ppm以上であると
、上記の含有物の凝集沈澱が効果的に行われ、約500
ppm以下であるとその凝集沈澱効果が劣る。That is, when the silicic acid concentration in the wastewater is about 500 ppm or more, the above-mentioned contents are effectively coagulated and precipitated, and about 500 ppm or more
If it is less than ppm, the coagulation and sedimentation effect will be poor.
従って本発明の方法においては、油廃水中のけい酸濃度
が約500ppm以上になる如く水溶性けい酸塩が添加
される。Therefore, in the method of the present invention, water-soluble silicates are added such that the silicic acid concentration in the oil wastewater is about 500 ppm or more.
また本発明の方法の対象とされる油廃水はけい酸を含む
ものであるが、このけい酸がイオン状、即ち溶液状また
はゾル若しくはこれに近い状態のコロイド状で水中によ
く分散していることが望ましく、その濃度が約500p
pm以上の場合は水溶性けい酸塩の添加を省略してもよ
い。Furthermore, the oil wastewater that is the subject of the method of the present invention contains silicic acid, and it is known that this silicic acid is well dispersed in water in ionic form, that is, in the form of a solution, or in the form of a sol or a colloid close to this. Desirably, the concentration is about 500p.
pm or more, the addition of water-soluble silicate may be omitted.
この発明の方法において、廃水に添加される水溶性アル
ミニウム塩の好ましい例として、ポリ塩化アルミニウム
および硫酸アルミニウムがあげられる。Preferred examples of water-soluble aluminum salts added to the wastewater in the method of this invention include polyaluminum chloride and aluminum sulfate.
この発明の方法においては、廃水に水溶性けい酸アルミ
ニウムおよび水溶性アルミニウム塩が添加された後、消
石灰を加えてpHを10〜12.5好ましくは11.5
〜12に調整された後、生成した沈澱が除去される。In the method of this invention, after water-soluble aluminum silicate and water-soluble aluminum salt are added to wastewater, slaked lime is added to adjust the pH to 10-12.5, preferably 11.5.
After adjusting to ~12, the formed precipitate is removed.
沈澱除去に先立って、必要に応じて廃水にポリ塩化アル
ミニウム以外の高分子凝集剤、例えばポリアクリル酸ナ
トリウム、ポリスチレンスルホン酸す) IJウム、水
溶性尿素樹脂等、が更に添加される。Prior to removing the precipitate, a polymer flocculant other than polyaluminum chloride, such as sodium polyacrylate, polystyrene sulfonate, water-soluble urea resin, etc., is further added to the wastewater as required.
凝集沈澱物を除去した廃水は、次に硫酸、塩酸等の鉱酸
でpHを6〜8に調整した後、活性炭、活性白土等の固
形吸着剤の層を通過せしめるか、またはこれらと共に撹
拌し、固形吸着剤に接触せしめられ、残存有機性物質が
除去される。The wastewater from which the coagulated sediment has been removed is then adjusted to pH 6 to 8 with mineral acids such as sulfuric acid and hydrochloric acid, and then passed through a layer of solid adsorbents such as activated carbon and activated clay, or stirred with them. , and contacted with a solid adsorbent to remove residual organic substances.
この発明の方法における各種の薬剤添加の各段階におい
ては、添加剤との均一な混合、反応、沈澱の凝集熟成を
促進する為に、所要の攪拌、場合によっては所要の加熱
、が行われることは勿論である。In each step of adding various chemicals in the method of this invention, necessary stirring and, in some cases, necessary heating, are performed in order to promote uniform mixing with additives, reaction, and coagulation and ripening of precipitates. Of course.
この発明の以上の如く詳述した方法により、油廃水中の
金属、特に亜鉛を0.lppm以下、n−ヘキサン抽出
物質を1 ppm以下、BODおよびCODを20pp
mとし、優れた処理効果を示すことができる。By the method of this invention as detailed above, metals, especially zinc, in oil wastewater can be removed to zero. lppm or less, n-hexane extractables less than 1 ppm, BOD and COD 20 ppm
m, and an excellent treatment effect can be shown.
以下この発明による方法を実施例に基いて更に詳述する
。The method according to the present invention will be explained in more detail below based on Examples.
次の実施例及び比較例においては、第1表の油廃水を使
用した。In the following Examples and Comparative Examples, oil wastewater from Table 1 was used.
註:いずれも自動車製造工業の工程廃水である。Note: All of these are process wastewater from the automobile manufacturing industry.
実施例 1
油廃水Aに該廃水中のSiO□濃度を500ppm増加
するようにけい酸ナトリウムを添加し、ついでポリ塩化
アルミニウムおよび消石灰がそれぞれ11000ppに
なる如く添加しpHを12.4とし、130rpmで5
分間攪拌し、ついでポリアクリル酸ナトリウムを1−に
なる如く添加し、回転数を3Orpmとして10分間攪
拌し、20分間静置した。Example 1 Sodium silicate was added to oil wastewater A so as to increase the SiO□ concentration in the wastewater by 500ppm, and then polyaluminum chloride and slaked lime were each added to 11,000pp to adjust the pH to 12.4, and the mixture was heated at 130 rpm. 5
The mixture was stirred for 1 minute, and then sodium polyacrylate was added in an amount of 1-, and the mixture was stirred for 10 minutes at a rotational speed of 3 Orpm, and left to stand for 20 minutes.
ろ紙にて沢過し、凝集沈澱物を除去した後、ン戸液に硫
酸を添加してpHを7.0とし、13.Orpmで2分
間攪拌し、つぎに活性炭層を通過せしめた。After filtering through filter paper to remove coagulated precipitates, sulfuric acid was added to the solution to adjust the pH to 7.0, and 13. The mixture was stirred at Orpm for 2 minutes and then passed through a layer of activated carbon.
得られた処理液の分析値を、以下の実施例、比較例と共
に第2表に示す。The analytical values of the obtained treatment liquid are shown in Table 2 together with the following Examples and Comparative Examples.
実施例 2 油廃水Bに実施例1と同様の処理を行った。Example 2 Oil wastewater B was treated in the same manner as in Example 1.
実施例 3
油廃水Bにけい酸ナトリウムを添加しない以外は実施例
1と同じ処理を行った。Example 3 The same treatment as in Example 1 was performed except that sodium silicate was not added to oil wastewater B.
実施例 4
活性炭に代えて活性白土を使用した以外は実施例1と同
じ処理を行った。Example 4 The same treatment as in Example 1 was performed except that activated clay was used instead of activated carbon.
実施例 5
活性炭に代えて活性白土を使用した以外は実施例2と同
じ処理を行った。Example 5 The same treatment as in Example 2 was performed except that activated clay was used instead of activated carbon.
比較例 1
油廃水Aに硫酸を添加し、pHを5とし、130ppm
で3分間攪拌し、ポリ塩化アルミニウムが2000pp
mになるように添加し、更に3分間攪拌、炭酸ナトリウ
ムを添加してpHを8.6とし、つぎにポリアクリル酸
ナトリウムを1 ppmになる如く添加し、40rpm
で10分間攪拌後20分間静置し、凝集沈澱物をろ紙に
て側渦した。Comparative Example 1 Sulfuric acid was added to oil wastewater A to adjust the pH to 5 and make it 130 ppm.
Stir for 3 minutes at
m, stirred for another 3 minutes, added sodium carbonate to adjust the pH to 8.6, then added sodium polyacrylate to 1 ppm, and stirred at 40 rpm.
After stirring for 10 minutes, the mixture was allowed to stand for 20 minutes, and the flocculated precipitate was side-vortexed using filter paper.
比較例 2 油廃水Bについて比較例1と同様に処理した。Comparative example 2 Oil wastewater B was treated in the same manner as in Comparative Example 1.
註:比較例2の供試油廃水Bはけい酸を752ppm含
有しているため比較的よい処理効果を示している。Note: Sample oil wastewater B of Comparative Example 2 contains 752 ppm of silicic acid, and thus shows a relatively good treatment effect.
この発明による廃水の浄化方法は以上の如くであるので
、けい酸および金属塩を含有する油廃水から、金属、油
およびBOD、CODで表示される有機性汚染物質を効
果的に除去することができるので、自動車製造工業、産
業機械工業等の事業所の製造工程から排出される油廃水
の浄化処理に極めて有効であり、産業上利用価値が大で
ある。As described above, the wastewater purification method according to the present invention can effectively remove metals, oil, and organic pollutants expressed as BOD and COD from oil wastewater containing silicic acid and metal salts. Therefore, it is extremely effective in purifying oil wastewater discharged from manufacturing processes in business establishments such as automobile manufacturing industry and industrial machinery industry, and has great industrial utility value.
Claims (1)
のけい酸濃度が約500ppm未満である場合には水溶
性けい酸塩を添加して、けい酸濃度を約500ppm以
上とした後、水溶性アルミニウム塩および消石灰を添加
してpHを10〜12.5とし、生成した沈澱を除去し
た後、鉱酸を添加してpHを6〜8とし、固形吸着剤を
接触せしめることを特徴とする廃水の浄化処理方法。 2 前記の油廃水に含まれるけい酸がイオン状および/
またはコロイド状けい酸であり、金属塩が亜鉛および/
または鉄の塩類である特許請求の範囲第1項の廃水の浄
化処理方法。 3 前記水溶性けい酸塩がけい酸ナトリウムである特許
請求の範囲第1項の廃水の浄化処理方法。 4 前記水溶性アルミニウム塩がポリ塩化アルミニウム
または硫酸アルミニウムであり、消石灰を添加したとき
にpHが11.5〜12であることを特徴とする特許請
求の範囲第1項の廃水の浄化方法。 5 前記固形吸着剤が活性炭又は活性白土である特許請
求の範囲第1項の廃水の浄化方法。[Claims] 1. If the silicic acid concentration in the wastewater is less than about 500 ppm, water-soluble silicate is added to oil wastewater containing silicic acid and metal salts to reduce the silicic acid concentration to about 500 ppm. After adjusting the pH to 500 ppm or more, water-soluble aluminum salt and slaked lime are added to adjust the pH to 10 to 12.5. After removing the generated precipitate, mineral acid is added to adjust the pH to 6 to 8, and the solid adsorbent is adjusted to 10 to 12.5. A wastewater purification method characterized by contacting the wastewater. 2 The silicic acid contained in the oil wastewater is ionic and/or
or colloidal silicic acid, the metal salts being zinc and/or colloidal silicic acid;
or iron salts, the method for purifying wastewater according to claim 1. 3. The method for purifying wastewater according to claim 1, wherein the water-soluble silicate is sodium silicate. 4. The method for purifying wastewater according to claim 1, wherein the water-soluble aluminum salt is polyaluminum chloride or aluminum sulfate, and has a pH of 11.5 to 12 when slaked lime is added. 5. The method for purifying wastewater according to claim 1, wherein the solid adsorbent is activated carbon or activated clay.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2131279A JPS5948154B2 (en) | 1979-02-27 | 1979-02-27 | Wastewater purification method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2131279A JPS5948154B2 (en) | 1979-02-27 | 1979-02-27 | Wastewater purification method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS55114388A JPS55114388A (en) | 1980-09-03 |
| JPS5948154B2 true JPS5948154B2 (en) | 1984-11-24 |
Family
ID=12051627
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2131279A Expired JPS5948154B2 (en) | 1979-02-27 | 1979-02-27 | Wastewater purification method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5948154B2 (en) |
Families Citing this family (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2006056022A1 (en) * | 2004-11-26 | 2006-06-01 | Hardman Australia Pty Ltd | Water treatment process |
| JP2008173610A (en) * | 2007-01-22 | 2008-07-31 | Mhi Environment Engineering Co Ltd | Waste liquid treatment method and waste liquid treatment system |
| FR2930541B1 (en) | 2008-04-29 | 2010-05-21 | Solvay | PROCESS FOR PURIFYING AQUEOUS SOLUTIONS |
| JP5731794B2 (en) * | 2010-11-02 | 2015-06-10 | アクアス株式会社 | Coagulation treatment method for high-concentration silica-containing water |
| CN112062249B (en) * | 2020-09-22 | 2022-07-29 | 神美科技有限公司 | Silicon removal medicament, preparation method and application thereof |
-
1979
- 1979-02-27 JP JP2131279A patent/JPS5948154B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS55114388A (en) | 1980-09-03 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| JP2000084568A (en) | Treatment method for resin-containing wastewater | |
| JP4293520B2 (en) | Fluorine ion removal method and remover | |
| JP4508600B2 (en) | Method and apparatus for treating fluorine-containing wastewater | |
| JPS5948154B2 (en) | Wastewater purification method | |
| JP2010075928A (en) | Treatment method and treatment device for fluorine-containing waste water | |
| JPH0144363B2 (en) | ||
| JP2003320376A (en) | Treatment method for fluorine-containing wastewater and chemical agent used therein | |
| JPH04322784A (en) | Treatment of waste processing liquid for photosensitive material | |
| JP2003112004A (en) | Flocculation method | |
| RU2792510C1 (en) | Method for purification of multicomponent industrial wastewater containing zinc and chromium | |
| RU2104316C1 (en) | Method for precipitation of ions of heavy metals from industrial sewage waters | |
| JPH1110169A (en) | Wastewater treatment method | |
| JPS6071083A (en) | Removal of heavy metal in waste water | |
| JP3501843B2 (en) | Treatment of oil-containing wastewater | |
| RU2778688C2 (en) | Technical means for purification of industrial effluents | |
| JP3267948B2 (en) | Treatment method for oil-containing waste liquid | |
| JPS6333881B2 (en) | ||
| JP2000325968A (en) | Treatment method of flue gas desulfurization wastewater treatment sludge | |
| JP3173981B2 (en) | Waste liquid treatment method | |
| JPH1076275A (en) | Wastewater treatment agent | |
| JPS6391193A (en) | Treatment of sewage containing calcium | |
| JP4187201B2 (en) | Aggregation method | |
| JP2005052798A (en) | Method of treating fluorine-containing sludge | |
| JPH0852477A (en) | How to treat papermaking wastewater | |
| JPS6355997B2 (en) |