WO2005075363A1 - Borofluoric acid-trapping agent and method of treating wastewater with the same - Google Patents

Borofluoric acid-trapping agent and method of treating wastewater with the same Download PDF

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Publication number
WO2005075363A1
WO2005075363A1 PCT/JP2005/001984 JP2005001984W WO2005075363A1 WO 2005075363 A1 WO2005075363 A1 WO 2005075363A1 JP 2005001984 W JP2005001984 W JP 2005001984W WO 2005075363 A1 WO2005075363 A1 WO 2005075363A1
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Prior art keywords
group
general formula
acid
wastewater
carbon atoms
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PCT/JP2005/001984
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French (fr)
Japanese (ja)
Inventor
Akira Yoshida
Yoshinori Iizawa
Original Assignee
Chugai Photo Chemial Co., Ltd.
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Priority to JP2005517818A priority Critical patent/JP4682043B2/en
Publication of WO2005075363A1 publication Critical patent/WO2005075363A1/en

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
    • C02F1/56Macromolecular compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/12Halogens or halogen-containing compounds
    • C02F2101/14Fluorine or fluorine-containing compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/12Nature of the water, waste water, sewage or sludge to be treated from the silicate or ceramic industries, e.g. waste waters from cement or glass factories
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • C02F2103/346Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from semiconductor processing, e.g. waste water from polishing of wafers

Definitions

  • the present invention relates to a process for treating wastewater containing borofluoride.
  • the present invention relates to an additive and a method for treating the same, and
  • the present invention relates to a treatment method for treating wastewater containing citrate in a short time without heating with external energy.
  • Fluorine compounds represented by hydrofluoric acid are valuable substances that are used in large quantities in industries such as chemical plants, semiconductor manufacturing, metal processing, glass processing, and plating. Due to its harmfulness, wastewater containing them has emission standard values, and strict emission regulations are being enforced.
  • As a general method for removing fluorine from wastewater calcium compounds such as slaked lime and calcium chloride are added to fluorine-containing wastewater, and the pH is adjusted to precipitate hardly soluble calcium fluoride. The method of solid-liquid separation is adopted.
  • emission standards are set for boron because of its harmfulness, and it is necessary to remove boron from wastewater when discharging.
  • a common method for removing boron is to use a calcium compound and aluminum compound.
  • a method is known in which a hardly soluble compound is formed depending on the substance, and sedimentation is separated.
  • boron as in the case of fluorine, it is difficult to remove boron when boron is present as borofluoride.
  • the following technology is disclosed as a method for treating borofluoride.
  • the present invention solves the above-mentioned drawbacks of the conventional treatment method, and provides a treatment agent capable of treating borohydrofluorate-containing wastewater at ordinary temperature and in a short time without generating a large amount of sludge. It is to provide a processing method.
  • the object of the present invention is solved by the following means (1) to (9).
  • An additive for removing borofluoric acid from wastewater comprising at least one compound represented by the following general formulas (1) to (4).
  • R i to R 4 each independently represent an alkyl group, an alkenyl group, a phenyl group or a benzyl group having 1 to 24 carbon atoms, and RR may be linked to each other to form a ring.
  • A represents an anionic polymer.
  • R i is an alkyl group having 1 to 24 carbon atoms, an alkenyl group, a phenyl group or Represents a benzyl group.
  • Z represents an atomic group necessary for constituting a hetero ring.
  • X- represents an anion.
  • Z AR represents an alkyl group having 1 to 24 carbon atoms, an alkyl group, a phenol group or a benzyl group. Z represents an atomic group necessary for constituting a hetero ring. A represents an anionic polymer.
  • a of the borofluoric acid scavenger represented by the general formulas (2) and (4) has a structure selected from the following group A.
  • Group A Alginic acid, pectin, gelatin, anionized starch, carboxymethylcellulose, polyacrylic acid, copolymer of acrylamide and acrylic acid
  • the mole number of the anionic moiety of the anionic polymer is from 0.01 to 5.0 moles per mole of the quaternary ammonium salt.
  • a wastewater treatment method for removing borofluoric acid from wastewater containing borohydrofluoric acid comprising the steps of: capturing fluorinated acid represented by the following general formula (1) or (3) in the wastewater; Wastewater treatment method characterized by adding at least one kind of agent.
  • R i to R 4 each independently represent an alkyl group, alkenyl group, phenyl group or benzyl group having 1 to 24 carbon atoms, and R 4 to R 4 may be linked to each other to form a ring.
  • X— represents an anion.
  • (6) After adding at least one of the borofluoric acid scavengers represented by the general formula (1) or (3), diatomaceous earth, bentonite, kaolin, activated carbon, po / le-trandoseme Wastewater treatment as described in (4) or (5), wherein at least one compound selected from the group consisting of a polymer, a hydrophilic polymer compound, a polyvalent metal, and a rare earth compound is added.
  • Wastewater treatment characterized by contacting wastewater containing borofluoride with a borofluoric acid scavenger represented by the general formula (2) or (4) below ⁇ 5 Method.
  • R ⁇ 4 f each independently an alkyl group with carbon number 1-2 4, an alkenyl group, an Fueyuru group or a benzyl group, it may also form a form a ring R i R each other les.
  • A represents an aionic polymer selected from Group A below.
  • Group A a / reginic acid, pectin, gelatin, aeonized starch, cal. Boxymethizolesenorelose, polyacrylic acid, copolymer of acrylamide and acrylic acid
  • R represents an alkyl group having 1 to 24 carbon atoms, an arcel group, a fuel group or a benzinole group.
  • Z represents an atomic group necessary for constituting a hetero ring.
  • A represents an anionic polymer.
  • R i to R 4 each independently represent an alkyl group having 1 to 24 carbon atoms, an alkyl group, a phenyl group or a benzyl group, and R i to R 4 are connected to each other to form a ring; Is also good.
  • A represents an ionic polymer.
  • Ri represents an alkyl group having 1 to 24 carbon atoms, an alkenyl group, a phenyl group or a benzinole group.
  • Z represents an atom group necessary for constituting a hete ring.
  • A represents an anionic polymer.
  • borofluoric acid scavenger of claims 1, 2, and 3 of the present invention By using the borofluoric acid scavenger of claims 1, 2, and 3 of the present invention, a small amount of sludge can be obtained from wastewater containing borofluoride without using external energy such as heating. Fluorine and boron in a short time Can be removed. In addition, there is no need to reinforce equipment such as installing a tank for secondary treatment (advanced treatment), and advanced treatment can be performed using only existing primary treatment equipment.
  • solid solution separation can be efficiently performed by sedimentation of the inert compound.
  • the flocculence of the floc is increased, and the sludge volume can be reduced.
  • the scavenger can be regenerated very efficiently, and a very economical borofluoride decomposition treatment can be performed.
  • Wastewater containing borohydrofluoric acid is discharged from, for example, metalworkers, glass processors, printed circuit board processors and metal surface treatment companies.
  • the present invention is characterized in that borofluoric acid scavengers represented by the following general formulas (1) to (4) are added to waste water containing borofluoride. Furthermore, the method is characterized in that a scavenger represented by the general formula (2) or (4), which has trapped borofluoric acid, is regenerated by contacting the scavenger with an aqueous solution adjusted to pH 8 or more.
  • R i to R 4 are each independently an alkyl group having 1 to 24 carbon atoms, an alkyl group, a phenyl group or Represents a benzyl group, and R to shaku may be linked to each other to form a ring. At least one of R i to R 4 preferably has an anoalkyl group or an anorecenyl group having 12 or more carbon atoms.
  • R represents an alkyl group having 1 to 24 carbon atoms, an alkenyl group, a phenyl group or a benzyl group.
  • Z represents an atomic group necessary for constituting a hetero ring.
  • X represents an anion.
  • R represents an alkyl group having 1 to 24 carbon atoms, an alkenyl group, a phenyl group or a benzyl group.
  • Z represents an atomic group necessary for constituting a hetero ring.
  • A represents an anionic polymer.
  • quaternary ammonium salt used in the present invention include dimethylstearenol-benzinoleum ummonium chloride, trimethyl lanyl ammonium ummonium chloride, and trimethyl cetyl ummonium chloride.
  • Trimethylsilyl armonium chloride, dimethinoresistorinoleammonium chloride, dimethinoreggioleinoleammonium chloride, methyl chloride tridodecinoleammonium chloride, benzalkonium chloride, 1-stearyl-1,4,4-trimethylbiperazinium and the like can be mentioned, but not limited thereto.
  • X in the general formula (1) represents an anion.
  • the anion, F-, CI -, B-, I-, S 0 4 2 -, N 0 3 2 -, C 0 3 2 -, P 0 4 2 - and the like can Rukoto cited.
  • a in the general formula (2) represents an anionic polymer.
  • the aionic polymer include alginic acid, pectin, gelatin, anionized starch, carboxymethylcellulose, polyacrylic acid, and copolymers of acrylamide and acrylic acid. Any material can be used as long as it forms a counter-ion with the quaternary ammonium salt represented by the general formula (2) to form a poorly water-soluble solid.
  • R i is an alkyl group having 1 to 24 carbon atoms and alkenyl, respectively.
  • those having an alkyl or alkenyl group having 8 or more carbon atoms are preferable, and those having an alkyl group or an alkyl group having 12 or more carbon atoms can be suitably used.
  • Z represents an atom group necessary for constituting a hetero ring, and is particularly preferably an atomic group necessary for constituting a pyridyl ring.
  • nitrogen-containing heterocyclic compound having a nitrogen quaternized by a substituent used in the present invention include laurylpyridinium chloride, cetylpyridinum chloride, and 1-stearyl 1H-base. But not limited thereto.
  • the amount of the borofluoric acid scavenger represented by the general formula (1) or (3) is 0.1 to 5.0, preferably 0.2, per mole of borofluoric acid ions contained in the wastewater.
  • the amount is 5 to 2.5 moles, more preferably 0.5 to 2.0 moles, and may be added in accordance with the desired removal rate of hydrofluorofluoride.
  • solid-liquid separation into treated water and insoluble compounds makes it possible to remove borofluoride from wastewater.
  • sedimentation separation, press filtration, centrifugal filtration, centrifugation, and the like are used as a method of solid-liquid separation.
  • diatomaceous earth, bentonite, kaolin, activated carbon, Portland cement, and hydrophilic high-molecular-weight compound are used to precipitate the insoluble compounds of borofluoride and quaternary ammonium salt and efficiently perform solid-liquid separation. It is preferable to add at least one compound selected from molecular compounds, polyvalent metals, and rare earth compounds. These compounds may be used alone or as a mixture of a plurality of compounds. The addition amount of these compounds is 0.0 0 0 5 5 treated water 0 wt 0/0, preferably 0.0 0 1 to 3.0 wt 0/0, more preferably 0.0 0 5 to 2.0% by weight.
  • hydrophilic polymer compound used in the present invention examples include alginic acid, pectin, gelatin, agar, anionized starch, carboxymethylcellulose, polyacrylic acid, polyethyleneimine, polyacrylamide, Examples include, but are not limited to, copolymers of acrylamide and acrylic acid and metal salts thereof, aluminum polychloride, polyiron sulfate, and polyiron chloride. Both natural products and synthetic products can be used, but those having biodegradability are preferable from the viewpoint of environmental protection.
  • Examples of the polyvalent metal used in the present invention include iron compounds such as iron chloride and iron sulfate, aluminum compounds such as aluminum chloride and sulfate bands, and zinc compounds such as zinc chloride and zinc sulfate. It is not done.
  • the rare earth compounds used in the present invention include cerium, lanthanum, Chloride, sulfate, nitrate, acetate such as sodium, prasedium, samarium, gadolinium, terbium, yttrium, etc., but are not limited thereto.
  • the borofluoric acid scavenger represented by the general formula (2) or (4) may be added directly to the waste water, or a packed bed may be formed and the waste water may be passed through the bed.
  • the hydrofluoric acid scavenger represented by the general formula (2) or (4) is quaternized by an aqueous solution or a substituent of a quaternary ammonium salt represented by the general formula (1) or (3).
  • an anionic polymer corresponding to A in the general formula (2) or an aqueous solution thereof is used.
  • the quaternary ammonium salt or the nitrogen-containing heterocyclic compound having nitrogen quaternized by a substituent and the anionic polymer can be mixed in any ratio, but preferably a quaternary ammonium salt or nitrogen-containing compound.
  • the mole ratio of the anionic moiety is from 0.01 mol to 5.0 mol, preferably from 0.1 mol to 2.5 mol, per 1 mol of the heterocyclic compound.
  • Alginic acid may be only mannuronic acid, only gnoleronic acid, or a random form thereof, and those having a polymerization degree of about 200 to 800 are preferably used.
  • Pectin is a linear polysaccharide composed of D-galacturonic acid, and a part of the carboxylic acid is a methyl ester.
  • High methoxypectin having a degree of esterification of 50% or less_b and low methoxypectin having a degree of esterification of 50% or less can be suitably used.
  • Gelatin is composed of one amino acid and imino acid linked by a peptide bond, and has various amino acid components. Glycine, proline, and hydroxyproline occupy a molecular weight of 1Z2 or more. The average molecular weight is from 200,000 to 200,000 or more, and among them, those having a molecular weight of 50,000 to 150,000 are particularly preferable.
  • carboxymethyl starch or phosphorylated starch in which an anionic functional group is introduced into the hydroxyl group of the glucose portion of the starch, such as a carboxymethyl group or a phosphonic acid group, is preferable.
  • an anionic functional group is introduced into the hydroxyl group of the glucose portion of the starch, such as a carboxymethyl group or a phosphonic acid group.
  • the carboxymethyl cellulose is not particularly specified, but those having a carboxyl substitution degree of 0.5 to 2.0 per Darcos unit can be suitably used.
  • polyacrylic acid a polymer obtained by polymerizing acrylic acid and Z or a salt thereof is used.
  • Acrylic acid can be polymerized by a persulfate such as ammonium persulfate, persulfuric acid or the like, or a redtus catalyst comprising a combination of a persulfate / reducing agent.
  • polymerization may be performed by visible light, ultraviolet light, electron beam, or ⁇ -ray.
  • products produced by modifying a polyacrylate such as polymethyl acrylate with a caustic alkali can also be suitably used.
  • copolymer of acrylamide and acrylic acid those obtained by copolymerizing acrylamide with sodium acrylate or a cationic monomer can be suitably used.
  • Commercially available products are commercially available from Sanyo Chemical Industries, Ltd. under the trade name “Sunfloc® j”, and from Mitsui Cynamid Co., Ltd. under the trade name “SuperFlock®”.
  • Commercially available products are exemplified.
  • the scavenger obtained by the above method is directly poured into waste water containing borofluoride adjusted to a pH of less than 5 and stirred for a while, then solid-liquid is added to the water to be treated and the discharged material. Separation makes it possible to remove borofluoride from wastewater.
  • the scavenger of the general formula (2) or (4) used for removing borofluoride desorbs borofluoric acid by contact with a solution adjusted to a pH of 8 or more, and is used as a repeated scavenger. Can be used.
  • borofluoride can be removed, but fluorine and boron cannot be removed.
  • fluorine and boron are contained in the wastewater together with borofluoride, the fluorine is removed by a common method such as calcium treatment with canosome and aluminum, and then the method of the present invention is used. May be applied.
  • a compound capable of reacting with borofluoric acid to form a salt is added before the addition of the borofluoric acid scavenger of the present invention. It can also be precipitated as chloride and removed.
  • Compounds that form salts by reacting with borofluoric acid include potassium salts such as potassium chloride and potassium carbonate, and the addition of these salts can reduce borofluoric acid in the wastewater to some extent.
  • scavengers were prepared as follows.
  • a quaternary ammonium salt or a nitrogen-containing heterocyclic compound having a nitrogen quaternized by a substituent is dissolved in 1,000 ml of water in an amount shown in Table 1 below, and the aeonionic polymer compound is dissolved in water.
  • Gelatin (Gelatin manufactured by Nitta Gelatin Co., Ltd.)
  • Ayuon starch (Privine p-163, manufactured by Nippon Starch Co., Ltd.) Carboxymethylcellulose (Daiichi Kogyo Seiyaku Co., Ltd. Seguchigen) Polyacrylic acid (Aron, manufactured by Toa Gosei Co., Ltd.)
  • the analysis of fluorine in the treated water was performed by the lanthanum-arizarin complexon method specified in JisK0102, and the analysis of boron was measured by the methylene blue absorption spectrophotometry specified in jIsK0102.
  • the wastewater used for the treatment was water containing borohydride discharged from the Metzki plant.
  • the compounds of the general formulas (1) and (3) were added to the wastewater at a temperature of 100 ° m 1, and the mixture was stirred for 5 minutes and then allowed to stand. At this time, the treated water was found to be cloudy, and was further filtered through a 5 A filter paper. The filtrate was analyzed for fluorine and boron. As a comparative example, the same treatment was performed without using the compound of the general formula (1). Table 2 shows the processing results.
  • the use of the compound of the general formula (1) or the general formula (3) makes it possible to remove fluorine and boron, that is, borofluoride, in wastewater. If the amount of the compound of the general formula (1) or (3) is equal to or more than that of the borofluoride, the compound can be removed up to about 5 pm.
  • a copolymer of acrylamide and atarilic acid (RA-51, manufactured by Rasafloc Industrial Co., Ltd.) was added, and the mixture was stirred for 5 minutes and then allowed to stand. The sludge layer thickness at this time was compared. The results are shown in Table 3.
  • Sludge layer thickness The thickness of the sludge 10 minutes after the completion of the treatment step was visually checked. (Thickness of sludge and height of liquid to drainage) The ratio is described.
  • the fluorine concentration was 5 ppm or less and the boron concentration was 1 ppm or less. In all of the processing results in the present invention, the fluorine concentration was 5 ppm or less and the boron concentration was 1 ppm or less.
  • the use of the flocculation aid quickly flocculates and precipitates the poorly soluble substance formed by the borofluoride and the compound represented by the general formula (1) or (3). It becomes possible. Further, by using a polyvalent metal Z rare earth compound in combination, it is possible to increase the sedimentation speed and reduce the amount of sludge.
  • Boron hydrofluoric acid scavenger 1 was added to 1,000 ml of wastewater as shown in Table 4, and after stirring for 1 hour, solid-liquid separation was performed, and the fluorine and boron concentrations were measured. As a comparative example, the same operation was performed by adjusting the H of the waste water to 7.5 with NaOH. The results are shown in Table 4.
  • Example 27 Capture agent 6 l.o ppm 0.1 ppm
  • Example 37 Capture agent 16 1.4 ppm 0.3 ppm
  • Example 42 Scavenger 21 2.0 ppm 0.3 ppm As shown in Table 5, all scavengers can remove borofluoride.
  • the water can be passed through the borofluoric acid scavenger to remove borofluoride. However, when the amount of treated water exceeds a certain value, the removal rate decreases.
  • Example 7 After treating the wastewater of 7001 in Example 6, the filling tank was filled with a NaHO solution adjusted to pH10. After 30 minutes, the NaOH solution was discarded, washed with water and regenerated. The wastewater was treated according to Example 5 again using this filling tank. Table 7 shows the results.
  • the liquid obtained by removing the precipitate deposited as borofluoridium has the general formula ( 1) Trimethyl stearylammonium chloride is added as the compound represented by (1), and cetyl pyridium chloride is added as the compound represented by the general formula (3), and the mixture is stirred for 5 minutes. Diatomaceous earth 1 g / L as coagulant Aid B, stirred for 5 minutes, then copolymerized with acrylamide and acrylic acid as water-soluble polymer coagulant (RasaFlok Industries, Ltd.) RA-51) manufactured by Co., Ltd. was added, and the mixture was stirred for 5 minutes and then allowed to stand. As a result of measuring the fluorine concentration in the supernatant, the fluorine content was less than 8 ppm. Table 8 shows the results.
  • Trimethylene is added to 100 mL of wastewater as a compound represented by the general formula (1).
  • the additive used in the method for treating effluent containing borofluoride according to the present invention and the method for treating the effluent contain external energy such as heating from the effluent containing borofluoride. This is useful because fluorine and boron can be removed in a short time with a small amount of sludge without using it.
  • facilities such as installing tanks for secondary processing (advanced processing) This is useful because it does not need to be increased and advanced treatment can be performed only with the existing primary treatment equipment.

Abstract

A wastewater which contains a borofluoric acid salt and is discharged by a plater, glass processor, printed-wiring-board manufacturer, etc. can be made to be extremely easily treated efficiently with an existing apparatus at ordinary temperature in a short time while preventing sludge generation. The wastewater treatment can be attained with a borofluoric acid-trapping agent represented by the following general formula (1) or (2). General formula (1) (1) R1 to R4 each independently represents C1-24 alkyl, alkenyl, phenyl, or benzyl, provided that R1 to R4 may be bonded to one another to form a ring; and X- represents an anion. General formula (2) (2) R1 to R4 each independently represents C1-24 alkyl, alkenyl, phenyl, or benzyl, provided that R1 to R4 may be bonded to one another to form a ring; and A represents an anionic polymer.

Description

ホウフッ化水素酸捕捉剤及びそれを用いた排水処理方法 Borofluoric acid scavenger and wastewater treatment method using the same
技術分野 Technical field
本発明はホウフッ化水素酸塩を含有する排水の処理方法に使用する添 明  The present invention relates to a process for treating wastewater containing borofluoride.
加剤及びその処理方法に関するものであり、 更に詳しくはホウフッ化水 田 The present invention relates to an additive and a method for treating the same, and
素酸塩を含有する排水を外部エネルギーで加熱することなく、 且つ短時 間で処理する処理方法に関するものである。 The present invention relates to a treatment method for treating wastewater containing citrate in a short time without heating with external energy.
背景技術 Background art
フッ化水素酸を代表とするフッ素化合物は、 化学工場や半導体製造、 金属 ■ ガラスの加工、 メツキ加工等の業界に於いて大量に使用される有 用な物質であるが、 その人体 ·環境に対する有害性からそれらを含有す る排水には排出基準値が設けられ、 厳しい排出規制が行われている。 一般的な排水中のフッ素除去の方法と しては、 フッ素含有排水に消石 灰、 塩化カルシウム等のカルシウム化合物を添加し、 更に p Hを調整し て難溶性のフッ化カルシウムを沈殿させ、 固液分離する方法が採られて いる。  Fluorine compounds represented by hydrofluoric acid are valuable substances that are used in large quantities in industries such as chemical plants, semiconductor manufacturing, metal processing, glass processing, and plating. Due to its harmfulness, wastewater containing them has emission standard values, and strict emission regulations are being enforced. As a general method for removing fluorine from wastewater, calcium compounds such as slaked lime and calcium chloride are added to fluorine-containing wastewater, and the pH is adjusted to precipitate hardly soluble calcium fluoride. The method of solid-liquid separation is adopted.
しかしながら排水中のフッ素化合物が、 ホウフッ化水素酸塩として存 在する場合、 カルシウム化合物を添加しても難溶性の化合物は生成しな いためフッ素の除去は困難である。  However, when the fluorine compound in the wastewater exists as borohydrofluoride, even if the calcium compound is added, the hardly soluble compound is not generated, so that it is difficult to remove the fluorine.
更に、 ホウ素に関しても、その有害性から排出基準が設けられており、 排出に当たっては、 排水中からホウ素も除去する必要がある。  In addition, emission standards are set for boron because of its harmfulness, and it is necessary to remove boron from wastewater when discharging.
一般的なホウ素除去の方法は、 カルシウム化合物とアルミニゥム化合 物により難溶性の化合物を生成し、沈降分離する方法が知られているが、 これもフッ素と同様に、 ホウ素がホウフッ化水素酸塩として存在する場 合、 ホウ素の除去は困難である。 A common method for removing boron is to use a calcium compound and aluminum compound. A method is known in which a hardly soluble compound is formed depending on the substance, and sedimentation is separated. However, also in the case of boron, as in the case of fluorine, it is difficult to remove boron when boron is present as borofluoride.
これらの問題を解決するために、 ホウフッ化水素酸塩の処理方法とし て、 次のような技術が開示されている。  To solve these problems, the following technology is disclosed as a method for treating borofluoride.
( 1 ) アルミ化合物又は第 2鉄塩を添加してホウフッ化水素酸塩を分 解し、 次いでカルシウム化合物を添加して生成したフッ化カルシウムを 除去する方法 (特公昭 5 4— 1 8 0 6 4号公報参照)。  (1) A method in which an aluminum compound or a ferric salt is added to decompose borofluoride, and then a calcium compound is added to remove generated calcium fluoride (Japanese Patent Publication No. 54-180806) No. 4).
( 2 ) アルミニウム化合物を添加して、 ホウフッ化水素酸塩を酸性領 域で熱分解した後、 カルシウム化合物を加えて生成したフッ化カルシゥ ムを除去する方法 (特開昭 6 2 - 2 2 7 4 9 6号公報参照)。  (2) A method in which an aluminum compound is added to thermally decompose borohydrofluoride in an acidic region, and then a calcium compound is added to remove calcium fluoride generated (Japanese Patent Laid-Open No. 62-227). No. 496).
( 3 ) ホウフッ化水素酸塩含有排水に硫酸アルミニゥムを加えて 5 0 °C以上で反応させてホウフッ化水素酸イオンを分解した後、 炭酸カル シゥムを添加してフッ素をカルシウムと して固定化■ 除去する方法 (特 開平 7— 3 2 8 6 4 5号公報参照)。  (3) Aluminum sulfate is added to waste water containing borofluoride and reacted at 50 ° C or more to decompose borofluoride ions, and then calcium carbonate is added to fix fluorine as calcium. ■ Removal method (see Japanese Patent Publication No. Hei 7—3 286 645).
然し、 これらの方法はいずれもホウフッ化水素酸塩の分解を促進をす るために加熱を必要とする。 又、 非加熱での処理に於いては長時間の分 解時間を要する等の問題を抱えていた。  However, all of these methods require heating to accelerate the decomposition of the borofluoride. In addition, the non-heating treatment had problems such as requiring a long disintegration time.
又、 アルミニウム化合物を大過剰に使用すれば、 フッ素の除去性は高 まるが、 これは大量のスラッジの原因となり、 その処分方法が問題とな る。 発明の開示  If a large excess of the aluminum compound is used, the removal of fluorine is enhanced, but this causes a large amount of sludge, and the disposal method becomes a problem. Disclosure of the invention
本発明は、 上記のような従来の処理方法の欠点を改善し、 ホウフッ化 水素酸塩含有排水を、 大量のスラッジを発生させることなく、 常温 .短 時間で処理することが可能な処理剤及び処理方法を提供することである。 本発明の目的は下記 ( 1 ) 〜 ( 9 ) の手段によって解決される。The present invention solves the above-mentioned drawbacks of the conventional treatment method, and provides a treatment agent capable of treating borohydrofluorate-containing wastewater at ordinary temperature and in a short time without generating a large amount of sludge. It is to provide a processing method. The object of the present invention is solved by the following means (1) to (9).
( 1 ) 排水からホウフッ化水素酸を除去する添加剤で、 下記一般式 ( 1 ) ~ (4) で表される化合物の少なく とも 1種よりなることを特徴 とするホウフッ化水素酸捕捉剤。 (1) An additive for removing borofluoric acid from wastewater, comprising at least one compound represented by the following general formulas (1) to (4).
一般式 ( 1 )  General formula (1)
、 フ 形 成 ,
Figure imgf000005_0001
Figure imgf000005_0001
R i〜R 4は夫々独立に炭素数 1〜 2 4のアルキル基、 アルケニル基、 フエニル基又はベンジル基を表し、 R R が互いに連結して環を形 成してもよい。 Aはァニオン性高分子を表す。 R i to R 4 each independently represent an alkyl group, an alkenyl group, a phenyl group or a benzyl group having 1 to 24 carbon atoms, and RR may be linked to each other to form a ring. A represents an anionic polymer.
一般式 ( 3 ) z 、  General formula (3) z,
R1+N Z X一 R1 one + NZX one
C '  C '
R iは炭素数 1〜 2 4のアルキル基、 アルケニル基、 フエニル基又は ベンジル基を表す。 Zはへテロ環を構成するのに必要な原子群を表す。 X -は陰イオンを表す。 R i is an alkyl group having 1 to 24 carbon atoms, an alkenyl group, a phenyl group or Represents a benzyl group. Z represents an atomic group necessary for constituting a hetero ring. X- represents an anion.
一般式 (4)  General formula (4)
Ri―" Z
Figure imgf000006_0001
A R は炭素数 1〜 2 4のアルキル基、 ァルケ-ル基、 フエ-ル基又は ベンジル基を表す。 Zはへテロ環を構成するのに必要な原子群を表す。 Aはァニオン性高分子を表す。
Ri― "Z
Figure imgf000006_0001
AR represents an alkyl group having 1 to 24 carbon atoms, an alkyl group, a phenol group or a benzyl group. Z represents an atomic group necessary for constituting a hetero ring. A represents an anionic polymer.
( 2 ) —般式 ( 2) 及び一般式 (4) で表されるホウフッ化水素酸捕 捉剤の Aが下記の A群から選ばれる構造を有することを特徴とする ( 1 ) の手段に記載のホウフッ化水素酸捕捉剤。  (2) — The means of (1), wherein A of the borofluoric acid scavenger represented by the general formulas (2) and (4) has a structure selected from the following group A. The borohydrofluoric acid scavenger as described in the above.
A群 : アルギン酸、 ぺクチン、 ゼラチン、 ァニオン化でんぷん、 カル ボキシメチルセルロース、 ポリアクリル酸、 アタ リルァミ ドとアク リル 酸との共重合体  Group A: Alginic acid, pectin, gelatin, anionized starch, carboxymethylcellulose, polyacrylic acid, copolymer of acrylamide and acrylic acid
( 3 ) 4級アンモニゥム塩 1モルに対し、 ァニオン性高分子のァニォ ン性部位のモル数が 0. 0 1〜 5. 0モルの割合で作成されたことを特 徴とする ( 2) の手段に記載のホウフッ化水素酸捕捉剤。  (3) It is characterized in that the mole number of the anionic moiety of the anionic polymer is from 0.01 to 5.0 moles per mole of the quaternary ammonium salt. The borofluoric acid scavenger according to the means.
(4 ) ホウフッ化水素酸塩を含有する排水からホウフッ化水素酸を除 去する排水処理方法に関し、 該排水へ下記一般式 ( 1 ) 又は一般式 ( 3 ) で表されるホゥフッ化水素酸捕捉剤の少なく とも 1種を添加することを 特徴とする排水処理方法。  (4) A wastewater treatment method for removing borofluoric acid from wastewater containing borohydrofluoric acid, the method comprising the steps of: capturing fluorinated acid represented by the following general formula (1) or (3) in the wastewater; Wastewater treatment method characterized by adding at least one kind of agent.
一般式 ( 1 )
Figure imgf000007_0001
R i〜R 4は夫々独立に炭素数 1〜 2 4のアルキル基、アルケニル基、 フエニル基又はベンジル基を表し、 R 〜R 4が互いに連結して環を形 成してもよい。 X—は陰イオンを表す。 ( 6) 一般式 ( 1 ) 又は一般式 ( 3 ) で表されるホウフッ化水素酸捕 捉剤の少なく とも 1種を添加した後、 珪藻土、 ベントナイ ト、 カオリ ン、 活性炭、 ポ /レ トラン ドセメ ン ト、 親水性高分子化合物、 多価金属類、 希 土類化合物から選択される 1種以上の化合物を添加することを特徴とす る (4) 又は ( 5 ) の手段に記載の排水処理方法。
General formula (1)
Figure imgf000007_0001
R i to R 4 each independently represent an alkyl group, alkenyl group, phenyl group or benzyl group having 1 to 24 carbon atoms, and R 4 to R 4 may be linked to each other to form a ring. X— represents an anion. (6) After adding at least one of the borofluoric acid scavengers represented by the general formula (1) or (3), diatomaceous earth, bentonite, kaolin, activated carbon, po / le-trandoseme Wastewater treatment as described in (4) or (5), wherein at least one compound selected from the group consisting of a polymer, a hydrophilic polymer compound, a polyvalent metal, and a rare earth compound is added. Method.
( 7 ) 該 ί匕合物の添加量は被処理水の 0. 0 0 0 5〜 5. 0重量%で あることを特徴とする (6 ) の手段に記載の排水処理方法。  (7) The wastewater treatment method as described in the means (6), wherein the amount of the conjugation product is 0.0005 to 5.0% by weight of the water to be treated.
(8) ホウフッ化水素酸塩を含有する排水と、 一般式 ( 2) 又は一般 式 (4) で表されるホウフッ化水素酸捕捉剤を ρ Η 5未満で接触させる ことを特徴とする排水処理方法。  (8) Wastewater treatment characterized by contacting wastewater containing borofluoride with a borofluoric acid scavenger represented by the general formula (2) or (4) below ρΗ5 Method.
一般式 (2 )  General formula (2)
Figure imgf000008_0001
Figure imgf000008_0001
R 〜 4fま夫々独立に炭素数 1〜 2 4のアルキル基、アルケニル基、 フエュル基又はベンジル基を表し、 R i R が互いに連結して環を形 成してもよレ、。 Aは下記 A群から選ばれるァ-オン性高分子を表す。 R ~ 4 f or each independently an alkyl group with carbon number 1-2 4, an alkenyl group, an Fueyuru group or a benzyl group, it may also form a form a ring R i R each other les. A represents an aionic polymer selected from Group A below.
A群: ァ /レギン酸、 ぺクチン、 ゼラチン、 ァェオン化でんぷん、 カル. ボキシメチゾレセノレロース、 ポリアクリル酸、 アクリルアミ ドとアクリル 酸との共重合体  Group A: a / reginic acid, pectin, gelatin, aeonized starch, cal. Boxymethizolesenorelose, polyacrylic acid, copolymer of acrylamide and acrylic acid
一般式 (4 )  General formula (4)
Figure imgf000008_0002
R は炭素数 1〜 2 4のアルキル基、 ァルケエル基、 フエエル基又は ベンジノレ基を表す。 Zはへテロ環を構成するのに必要な原子群を表す。
Figure imgf000008_0002
R represents an alkyl group having 1 to 24 carbon atoms, an arcel group, a fuel group or a benzinole group. Z represents an atomic group necessary for constituting a hetero ring.
Aはァニオン性高分子を表す。 A represents an anionic polymer.
( 9) 下記一般式 ( 2) 又は一般式 (4) で表されるホウフッ化水素 酸捕捉剤の再生方法に関し、 ホウフッ化水素酸を捕捉した捕捉剤を p H 8以上に調整した水溶液と接触させることで再生することを特徴とする ホウフッ化水素酸捕捉剤の再生方法。  (9) Regarding the method for regenerating the borofluoric acid scavenger represented by the following general formula (2) or (4), contact the scavenger trapping borofluoric acid with an aqueous solution adjusted to pH 8 or more A method for regenerating a borofluoric acid scavenger, characterized in that the regenerating is performed by causing the fluorinated acid to be regenerated.
一般式 ( 2 )  General formula (2)
Figure imgf000009_0001
Figure imgf000009_0001
R i〜R 4は夫々独立に炭素数 I〜 2 4のアルキル基、 ァルケ-ル基、 フエ二ノレ基又はベンジル基を表し、 R i〜R 4が互いに連結して環を形 成しても よい。 Aはァ-オン性高分子を表す。 R i to R 4 each independently represent an alkyl group having 1 to 24 carbon atoms, an alkyl group, a phenyl group or a benzyl group, and R i to R 4 are connected to each other to form a ring; Is also good. A represents an ionic polymer.
一般式 ( 4) General formula (4)
Ri— +N Z A R iは炭素数 1〜 2 4のアルキル基、 アルケニル基、 フエニル基又は ベンジノレ基を表す。 Zはへテ口環を構成するのに必要な原子群を表す。 Ri— + NZ A Ri represents an alkyl group having 1 to 24 carbon atoms, an alkenyl group, a phenyl group or a benzinole group. Z represents an atom group necessary for constituting a hete ring.
Aはァニオン性高分子を表す。 A represents an anionic polymer.
本発明請求項 1, 2 , 3のホウフッ化水素酸捕捉剤を使用することに より、 ホウフッ化水素酸塩を含有する排水から、 加熱等の外部エネルギ —を使用することなく、 少ないスラッジ量で短時間にフッ素及ぴホウ素 を除去することができる。 更に、 2次処理 (高度処理) のための槽を設 置する等設備の増強の必要がなく、 既存の 1次処理設備のみで高度処理 が可能となる。 By using the borofluoric acid scavenger of claims 1, 2, and 3 of the present invention, a small amount of sludge can be obtained from wastewater containing borofluoride without using external energy such as heating. Fluorine and boron in a short time Can be removed. In addition, there is no need to reinforce equipment such as installing a tank for secondary treatment (advanced treatment), and advanced treatment can be performed using only existing primary treatment equipment.
又、 本発明請求項 4, 5によれば、 上述の効果をあげることが出きる と共に、 極めて簡単な操作及ぴ従来設備そのままの使用で所期の目的を 達成することができる。  According to claims 4 and 5 of the present invention, the above-mentioned effects can be obtained, and the intended purpose can be achieved by extremely simple operation and use of the conventional equipment as it is.
又、 本発明請求項 6 , 7によれば、 不活性化合物の沈降により、 固溶 分離を効率よく行うこと 出来る。 又、 フロックの凝集性が高まり、 ス ラッジの減容ができる。  According to claims 6 and 7 of the present invention, solid solution separation can be efficiently performed by sedimentation of the inert compound. In addition, the flocculence of the floc is increased, and the sludge volume can be reduced.
又、 本発明請求項 8によれば、 p H 5未満で接触排水をすることによ り、 除去剤の効率を更に向上させることができる。  According to claim 8 of the present invention, by performing contact drainage at a pH of less than 5, the efficiency of the removing agent can be further improved.
更に、 本発明請求項 9によれば、 捕捉剤の再生が極めて効率よく行わ れ、 極めて経済的なホウフッ化水素酸塩の分解処理が行える。 発明を実施する為の最良の形態  Furthermore, according to the ninth aspect of the present invention, the scavenger can be regenerated very efficiently, and a very economical borofluoride decomposition treatment can be performed. BEST MODE FOR CARRYING OUT THE INVENTION
以下、 本発明を詳細に説明する。  Hereinafter, the present invention will be described in detail.
本発明の排水の処理方法は、 ホウフッ化水素酸塩を含有した排水を対 象とする。 ホウフッ化水素酸塩を含有する排水は、 例えばメ ツキ加工業 者、 ガラス加工業者、 プリント基板加工業者、 金属表面処理業者などか ら排出される。  The wastewater treatment method of the present invention is intended for wastewater containing borofluoride. Wastewater containing borohydrofluoric acid is discharged from, for example, metalworkers, glass processors, printed circuit board processors and metal surface treatment companies.
本発明は、 ホウフッ化水素酸塩を含有する排水に、 下記一般式 ( 1 ) 〜 (4 ) で表されるホウフッ化水素酸の捕捉剤を添加することを特徴と する。 更には、 ホウフッ化水素酸を捕捉した一般式 ( 2 ) 又は (4 ) で 表される捕捉剤を、 p H 8以上に調整した水溶液と接触させることで再 生する方法を特徴とする。  The present invention is characterized in that borofluoric acid scavengers represented by the following general formulas (1) to (4) are added to waste water containing borofluoride. Furthermore, the method is characterized in that a scavenger represented by the general formula (2) or (4), which has trapped borofluoric acid, is regenerated by contacting the scavenger with an aqueous solution adjusted to pH 8 or more.
一般式 ( 1 ) General formula (1)
Figure imgf000011_0001
一般式 ( 2 )
Figure imgf000011_0001
General formula (2)
Figure imgf000011_0002
上記一般式 ( 1 )、 ( 2 ) で表される 4級アンモニゥム塩に於いて、 R i〜 R 4は夫々独立に炭素数 1〜 2 4のアルキル基、 ァルケ-ル基、 フ ェニル基又はベンジル基を表し、 R 〜尺^!が互いに連結して環を形成 してもよい。 R i〜R4のうち少なく とも 1種は炭素数 1 2以上のァノレ キル基又はァノレケニル基を持つものが好適に使用できる。
Figure imgf000011_0002
In the quaternary ammonium salts represented by the above general formulas (1) and (2), R i to R 4 are each independently an alkyl group having 1 to 24 carbon atoms, an alkyl group, a phenyl group or Represents a benzyl group, and R to shaku may be linked to each other to form a ring. At least one of R i to R 4 preferably has an anoalkyl group or an anorecenyl group having 12 or more carbon atoms.
一般式 ( 3 )  General formula (3)
RT N Z X RT N Z X
C '  C '
R は炭素数 1〜 2 4のアルキル基、 アルケニル基、 フエニル基又は ベンジル基を表す。 Zはへテロ環を構成するのに必要な原子群を表す。 X一は陰イオンを表す。 R represents an alkyl group having 1 to 24 carbon atoms, an alkenyl group, a phenyl group or a benzyl group. Z represents an atomic group necessary for constituting a hetero ring. X represents an anion.
一般式 (4 ) Ri— +N Z A General formula (4) Ri— + NZA
WCW C no
R は炭素数 1〜 2 4のアルキル基、 アルケュノレ基、 フエ-ル基又は ベンジル基を表す。 Zはへテロ環を構成するのに必要な原子群を表す。 Aはァニオン性高分子を表す。  R represents an alkyl group having 1 to 24 carbon atoms, an alkenyl group, a phenyl group or a benzyl group. Z represents an atomic group necessary for constituting a hetero ring. A represents an anionic polymer.
本発明に使用される 4級アンモニゥム塩の具体例と して、 ジメチルス テアリ ノレべンジノレアンモュゥムクロライ ド、 ト リ メチルラゥリルァンモ ニゥムクロライ ド、 ト リメチルセチルァクモウェムク口ライ ド、 ト リ メ チルステアリノレアンモニゥムクロライ ド、 ジメチノレジステアリノレアンモ ユウムクロライ ド、 ジメチノレジオレイノレアンモニゥムクロライ ド、 メチ ノレ ト リ ドデシノレアンモニゥムクロライ ド、 塩化ベンザルコニゥム、 1 - ステアリル一 1, 4, 4 一 トリメチルビペラジニゥム等を挙げることが 出来るがこれに限定されるものではない。  Specific examples of the quaternary ammonium salt used in the present invention include dimethylstearenol-benzinoleum ummonium chloride, trimethyl lanyl ammonium ummonium chloride, and trimethyl cetyl ummonium chloride. Trimethylsilyl armonium chloride, dimethinoresistorinoleammonium chloride, dimethinoreggioleinoleammonium chloride, methyl chloride tridodecinoleammonium chloride, benzalkonium chloride, 1-stearyl-1,4,4-trimethylbiperazinium and the like can be mentioned, but not limited thereto.
一般式 ( 1 ) の X—は陰ィオンを表す。 陰イオンとしては、 F―、 C I —、 B―、 I—、 S 0 4 2—、 N 0 3 2—、 C 0 3 2—、 P 0 4 2—等を挙げ ることが出来る。 X in the general formula (1) represents an anion. The anion, F-, CI -, B-, I-, S 0 4 2 -, N 0 3 2 -, C 0 3 2 -, P 0 4 2 - and the like can Rukoto cited.
一般式 ( 2 ) の Aはァニオン性高分子を表す。 ァ-オン性高分子の具 体例と して、 アルギン酸、 ぺクチン、 ゼラチン、 ァニオン化でんぷん、 カルポキシメチルセルロース、 ポリアク リル酸、 アク リルアミ ドとァク リル酸との共重合体等を挙げることが出来るが、 一般式 ( 2 ) で表され る 4級アンモユウム塩と対イオンを形成して難水溶性の固形物を形成で きれば何でもよい。  A in the general formula (2) represents an anionic polymer. Specific examples of the aionic polymer include alginic acid, pectin, gelatin, anionized starch, carboxymethylcellulose, polyacrylic acid, and copolymers of acrylamide and acrylic acid. Any material can be used as long as it forms a counter-ion with the quaternary ammonium salt represented by the general formula (2) to form a poorly water-soluble solid.
一般式 ( 3 )
Figure imgf000013_0001
一般式 (4)
General formula (3)
Figure imgf000013_0001
General formula (4)
Ri + ARi + A
Figure imgf000013_0002
Figure imgf000013_0002
一般式 (3)、 (4 ) で表される、 置換基によって 4級化された窒素を 持つ含窒素複素環化合物に於いて、 R iは夫々炭素数 1〜 2 4のアルキ ル基、 アルケニル基、 フエエル基又はベンジル基を表す。 特に、 炭素数 8以上のアルキル 又はアルケニル基を持つものが好適であり、 更に好 ましくは炭素数 1 2以上のアルキル基又はアルケ-ル基を持つものが好 適に使用できる。 Z はへテロ環を構成するのに必要な原子群を表し、 特 にピリジゥム環を構成するのに必要な原子群であることが好ましい。 本 発明に使用される置換基によって 4級化された窒素を持つ含窒素複素環 化合物の具体例と して、 ラウリルピリジニゥムクロライ ド、 セチルピリ ジユウムク口ライ ド、 1—ステアリー 1 H—べンゾィミダゾリ ゥム等が 挙げられるが、 これに限定するものではない。  In the nitrogen-containing heterocyclic compound having a nitrogen quaternized by a substituent represented by the general formulas (3) and (4), R i is an alkyl group having 1 to 24 carbon atoms and alkenyl, respectively. Represents a group, a fuel group or a benzyl group. In particular, those having an alkyl or alkenyl group having 8 or more carbon atoms are preferable, and those having an alkyl group or an alkyl group having 12 or more carbon atoms can be suitably used. Z represents an atom group necessary for constituting a hetero ring, and is particularly preferably an atomic group necessary for constituting a pyridyl ring. Specific examples of the nitrogen-containing heterocyclic compound having a nitrogen quaternized by a substituent used in the present invention include laurylpyridinium chloride, cetylpyridinum chloride, and 1-stearyl 1H-base. But not limited thereto.
一般式 ( 1 ) 又は ( 3) で表されるホウフッ化水素酸捕捉剤の添加量 は、排水中に含まれるホウフッ化水素酸イオン 1モルあたり 0. 1〜 5. 0、 好ましくは 0. 2 5〜 2. 5モル、 より好ましくは 0. 5〜 2. 0 モルであり、所望のホゥフッ化水素酸塩除去率に合せて添加すればよレ、。 被処理水に一般式 ( 1 ) 又は ( 3 ) で表されるホウフッ化水素酸捕捉剤 〖Q]+X—を添加する ことにより、 ホウフッ化水素酸と不溶性化合物を形 成する。 The amount of the borofluoric acid scavenger represented by the general formula (1) or (3) is 0.1 to 5.0, preferably 0.2, per mole of borofluoric acid ions contained in the wastewater. The amount is 5 to 2.5 moles, more preferably 0.5 to 2.0 moles, and may be added in accordance with the desired removal rate of hydrofluorofluoride. By adding borofluoric acid scavenger [Q] + X— represented by the general formula (1) or (3) to the water to be treated, borofluoric acid and an insoluble compound are formed. To achieve.
[Q]+X_ + N a +B F 4—→[Q]+B F 4— l + N a X [Q] + X _ + Na + BF 4 — → [Q] + BF 4 — l + Na X
上記行程で処理した後、 処理水と不溶性化合物に固液分離することに より、 排水中からホウフッ化水素酸塩を除去することが可能となる。 固 液分離の方法と しては、 沈降分離、 プレスろ過、 遠心濾過、 遠心分離等 が用いられる。  After the treatment in the above process, solid-liquid separation into treated water and insoluble compounds makes it possible to remove borofluoride from wastewater. As a method of solid-liquid separation, sedimentation separation, press filtration, centrifugal filtration, centrifugation, and the like are used.
本発明に於いて、 ホウフッ化水素酸塩と 4級アンモユウム塩の不溶性 化合物を沈降させ、 固液分離を効率よく行うために、 珪藻土、 ベントナ イ ト、 カオリ ン、 活性炭、 ポルトランドセメント、 親水性高分子化合物、 多価金属類、 希土類化合物から選択される少なく とも 1つの化合物を添 加することが好ましい。 これらの化合物は単独で用いてもよいし、 複数 の化合物を混合して用いてもよい。 これらの化合物の添加量は、 被処理 水の 0. 0 0 0 5〜 5. 0重量0 /0、好ましくは 0. 0 0 1〜 3. 0重量0 /0、 より好ましくは 0. 0 0 5〜 2. 0重量%である。 In the present invention, diatomaceous earth, bentonite, kaolin, activated carbon, Portland cement, and hydrophilic high-molecular-weight compound are used to precipitate the insoluble compounds of borofluoride and quaternary ammonium salt and efficiently perform solid-liquid separation. It is preferable to add at least one compound selected from molecular compounds, polyvalent metals, and rare earth compounds. These compounds may be used alone or as a mixture of a plurality of compounds. The addition amount of these compounds is 0.0 0 0 5 5 treated water 0 wt 0/0, preferably 0.0 0 1 to 3.0 wt 0/0, more preferably 0.0 0 5 to 2.0% by weight.
本発明に用いられる親水性高分子化合物の具体的な例として、 アルギ ン酸、 ぺクチン、 ゼラチン、 寒天、 ァニオン化でんぷん、 カルボキシメ チルセルロース、 ポリアク リル酸、 ポリエチレンィ ミン、 ポリアク リル アミ ド、 アクリルアミ ドとアクリル酸との共重合体及びその金属塩、 ポ リ塩化アルミニウム、 ポリ硫酸鉄、 ポリ塩化鉄などが挙げられるが、 こ れに限定されるものではない。天産品及び合成品の何れも使用できるが、 環境保全の観点からは生分解性を有するものが好ましい。  Specific examples of the hydrophilic polymer compound used in the present invention include alginic acid, pectin, gelatin, agar, anionized starch, carboxymethylcellulose, polyacrylic acid, polyethyleneimine, polyacrylamide, Examples include, but are not limited to, copolymers of acrylamide and acrylic acid and metal salts thereof, aluminum polychloride, polyiron sulfate, and polyiron chloride. Both natural products and synthetic products can be used, but those having biodegradability are preferable from the viewpoint of environmental protection.
本発明に用いられる多価金属としては、塩化鉄、硫酸鉄等の鉄化合物、 塩化アルミニウム、 硫酸バンド等のアルミニウム化合物、 塩化亜鉛、 硫 酸亜鉛等の亜鉛化合物等が挙げられるが、 これに限定されるものではな い。  Examples of the polyvalent metal used in the present invention include iron compounds such as iron chloride and iron sulfate, aluminum compounds such as aluminum chloride and sulfate bands, and zinc compounds such as zinc chloride and zinc sulfate. It is not done.
本発明に用いられる希土類化合物と しては、 セリ ウム、 ランタン、 ネ ォジゥム、 プラセォジゥム、 サマリ ウム、 ガドリニウム、 テルビウム、 イッ トリウム等の塩化物、 硫酸塩、 硝酸塩、 酢酸塩が挙げられるが、 こ れに限定されるものではない。 The rare earth compounds used in the present invention include cerium, lanthanum, Chloride, sulfate, nitrate, acetate such as sodium, prasedium, samarium, gadolinium, terbium, yttrium, etc., but are not limited thereto.
これらの化合物を添加することにより、 フロックの凝集性が高まり、 スラッジの減容が可能となる。  By adding these compounds, the flocculence of the floc is increased, and the volume of sludge can be reduced.
一般式 ( 2 ) 又は (4 ) で表されるホウフッ化水素酸の捕捉剤は、 直 接排水に添加してもよいし、 充填層を形成し、 その中に排水を通過させ てもよい。  The borofluoric acid scavenger represented by the general formula (2) or (4) may be added directly to the waste water, or a packed bed may be formed and the waste water may be passed through the bed.
一般式 ( 2 ) 又は (4 ) で表されるホウフッ化水素酸の捕捉剤は、 一 般式 ( 1 ) 又は ( 3 ) で表される 4級アンモニゥム塩の水溶液又は置換 基によって 4級化された窒素を持つ含窒素複素環化合物の水溶液と、 ァ 二オン性高分子を反応させることによって作成することができるが、 特 に一般式 (2 ) の Aに相当するァニオン性高分子又はその水溶液が好適 に使用でき、 これらを混合し、 生成した沈殿物を固液分離することで容 易に得られる。  The hydrofluoric acid scavenger represented by the general formula (2) or (4) is quaternized by an aqueous solution or a substituent of a quaternary ammonium salt represented by the general formula (1) or (3). Can be prepared by reacting an aqueous solution of a nitrogen-containing heterocyclic compound having a nitrogen with an anionic polymer. Particularly, an anionic polymer corresponding to A in the general formula (2) or an aqueous solution thereof is used. Can be suitably used, and they can be easily obtained by mixing these and subjecting the resulting precipitate to solid-liquid separation.
4級アンモユウム塩又は置換基によって 4級化された窒素を持つ含窒 素複素環化合物とァニオン性高分子は任意の割合で混合することができ るが、 好ましくは 4級アンモユウム塩、 又は含窒素複素環化合物 1モル に対して、 ァニオン性の部位のモル数が 0 . 0 1モル〜 5 . 0モルの割 合、 より好ましくは 0 . 1 モル〜 2 . 5モルの割合で混合することによ つて、 効率よく効果の高い捕捉剤を作成することができる。  The quaternary ammonium salt or the nitrogen-containing heterocyclic compound having nitrogen quaternized by a substituent and the anionic polymer can be mixed in any ratio, but preferably a quaternary ammonium salt or nitrogen-containing compound. The mole ratio of the anionic moiety is from 0.01 mol to 5.0 mol, preferably from 0.1 mol to 2.5 mol, per 1 mol of the heterocyclic compound. Thus, a highly effective scavenger can be efficiently produced.
アルギン酸と しては、 マンヌロン酸のみ、 グノレロン酸のみであっても、 これらランダム体であってもよく、 重合度 2 0 0〜 8 0 0程度のものが 好適に用いられる。  Alginic acid may be only mannuronic acid, only gnoleronic acid, or a random form thereof, and those having a polymerization degree of about 200 to 800 are preferably used.
ぺクチンは、 D—ガラク トウロン酸から成る直鎖状の多糖類であって、 カルボキシルキの一部がメチルエステルになっている。本発明に於いて、 エステル化度が 5 0 %以 _bであるハイメ トキシぺクチンも、 5 0 %以下 であるローメ トシキぺクチンも好適に使用することができる。 Pectin is a linear polysaccharide composed of D-galacturonic acid, and a part of the carboxylic acid is a methyl ester. In the present invention, High methoxypectin having a degree of esterification of 50% or less_b and low methoxypectin having a degree of esterification of 50% or less can be suitably used.
ゼラチンはぺプチド結合によって結合された 一アミノ酸及びィミノ 酸から構成されており、 アミノ酸成分は種々あるが、 グリシンとプロリ ン及ぴヒ ドロキシプロリ ンが分子量の 1 Z 2以上を占めている。 平均分 子量は 2 0, 0 0 0〜 2 0 0, 0 0 0以上であり、 このうち 5 0 , 0 0 0 - 1 5 0 , 0 0 0の分子量のものが特に好適である。  Gelatin is composed of one amino acid and imino acid linked by a peptide bond, and has various amino acid components. Glycine, proline, and hydroxyproline occupy a molecular weight of 1Z2 or more. The average molecular weight is from 200,000 to 200,000 or more, and among them, those having a molecular weight of 50,000 to 150,000 are particularly preferable.
ァェオン化でんぷんと しては、 でんぷんのグルコース部分の水酸基に ァニオン性の官能基を導入したものであって、 カルボキシメチル基ゃホ スホン酸基を導入した、 カルボキシメチルでんぷんやリン酸化でんぷん などが好適に使用できる。  As the aeon-modified starch, carboxymethyl starch or phosphorylated starch in which an anionic functional group is introduced into the hydroxyl group of the glucose portion of the starch, such as a carboxymethyl group or a phosphonic acid group, is preferable. Can be used for
カルボキシメチルセルロ ースとしては、 特に指定はないが、 ダルコ一 ス単位あたり、 カルボシキル置換度が 0 . 5〜 2 . 0のものが好適に使 用できる。  The carboxymethyl cellulose is not particularly specified, but those having a carboxyl substitution degree of 0.5 to 2.0 per Darcos unit can be suitably used.
ポリアクリル酸としては、 アクリル酸及び Z又はその塩を重合して得 られる重合体が用いられる。 アクリル酸を過硫酸アンモェゥム、 過硫酸 力リ ゥム等の過流酸塩、 又は過流酸塩/還元剤を組合わせてなるレツ ド タス触媒によって重合する ことができる。 又、 可視光線、 紫外線、 電子 線、 又は γ線によって重合してもよい。 又、 ポリアク リル酸メチル等の ポリアクリル酸エステルを苛性アルカリで鹼化することによって、 製造 した製品も好適に使用する ことができる。  As polyacrylic acid, a polymer obtained by polymerizing acrylic acid and Z or a salt thereof is used. Acrylic acid can be polymerized by a persulfate such as ammonium persulfate, persulfuric acid or the like, or a redtus catalyst comprising a combination of a persulfate / reducing agent. Further, polymerization may be performed by visible light, ultraviolet light, electron beam, or γ-ray. Further, products produced by modifying a polyacrylate such as polymethyl acrylate with a caustic alkali can also be suitably used.
アクリルアミ ドとアタ リ ル酸との共重合体は、 アタ リルァミ ドをァク リル酸ナトリゥム又はカチオン性モノマートと共重合して得られたもの が好適に使用することができる。 市販品としては、 三洋化成工業株式会 社から「サンフロック (登録商標) jの商品名で市販されている製品、 三 井サイナミッ ド株式会社から「スーパフロ ック (登録商標) 」の商品名で 市販されている製品などが挙げられる。 As the copolymer of acrylamide and acrylic acid, those obtained by copolymerizing acrylamide with sodium acrylate or a cationic monomer can be suitably used. Commercially available products are commercially available from Sanyo Chemical Industries, Ltd. under the trade name “Sunfloc® j”, and from Mitsui Cynamid Co., Ltd. under the trade name “SuperFlock®”. Commercially available products are exemplified.
上記のような方法で得られた捕捉剤を p H 5未満に調整されたホウフ ッ化水素酸塩を含有する排水に直接投入してしばらく撹拌した後、 被処 理水と排出材に固液分離することで排水からホウフッ化水素酸塩の除去 が可能となる。  The scavenger obtained by the above method is directly poured into waste water containing borofluoride adjusted to a pH of less than 5 and stirred for a while, then solid-liquid is added to the water to be treated and the discharged material. Separation makes it possible to remove borofluoride from wastewater.
又は、 該捕捉剤を除去塔に充填し、 ここに; p H 5以下に調整されたホ ゥフッ化水素酸塩を含有する排水を通水することでもホウフッ化水素酸 塩の除去が可能となる。  Alternatively, it is also possible to remove the borofluoride salt by filling the scavenger with a removal tower and passing the wastewater containing a hydrofluoride adjusted to pH 5 or less. .
ホウフッ化水素酸塩の除去に使用した一般式 ( 2 ) 又は一般式 (4 ) の捕捉剤は、 p H 8以上に調整した溶液と接触させることでホウフッ化 水素酸を脱着、 繰返し捕捉剤として使用することができる。  The scavenger of the general formula (2) or (4) used for removing borofluoride desorbs borofluoric acid by contact with a solution adjusted to a pH of 8 or more, and is used as a repeated scavenger. Can be used.
尚、 本発明の方法に於いて、 ホウフッ化水素酸塩は除去できるが、 フ ッ素、 ホウ素は除去できない。 排水中にホウフッ化水素酸塩と共に、 フ ッ素、 ホウ素を含有する場合は、 一般的な方法であるカルシウム処理に よりフッ素をカノレシゥムとアルミニウムによる処理でホウ素をそれぞれ 除去した後、 本発明の方法を適用してもよい。  In the method of the present invention, borofluoride can be removed, but fluorine and boron cannot be removed. When fluorine and boron are contained in the wastewater together with borofluoride, the fluorine is removed by a common method such as calcium treatment with canosome and aluminum, and then the method of the present invention is used. May be applied.
排水中にホウフッ化水素を多量に含む廃液の場合は、 本発明のホウフ ッ化水素酸捕足剤を添加する前に、 ホウフッ化酸と反応して塩を形成す る化合物を添加してホウフッ化塩として析出させ除去を行なうことも出 来る。 ホウフッ化酸と反応して塩を形成する化合物としては、 塩化カリ ゥム、炭酸カリ ウム等のカリ ゥム塩が挙げられ、 これらの添加によって、 排液中のホウフッ化水素酸をある程度低減でき、 この操作で取り切れな いホウフッ化酸を本発明の補足剤を使用する事で、 補足剤を効率よく使 用する事が出来る。  In the case of a waste liquid containing a large amount of hydrogen borofluoride in the wastewater, a compound capable of reacting with borofluoric acid to form a salt is added before the addition of the borofluoric acid scavenger of the present invention. It can also be precipitated as chloride and removed. Compounds that form salts by reacting with borofluoric acid include potassium salts such as potassium chloride and potassium carbonate, and the addition of these salts can reduce borofluoric acid in the wastewater to some extent. By using the fluorinated acid that cannot be removed by this operation with the supplement of the present invention, the supplement can be used efficiently.
本発明のホウフッ化補足剤は必要量以上添加しても、 ホウフッ化水素 酸除去能力に問題は生じないが、 排水中の C O D、 B O Dが高くなつて しまう事がある。 この場合、 ホウフッ化水素酸除去処理後に 4級アンモ ェゥム捕捉剤を加えることによって、 余剰のホウフッ化補足剤を除去す る事が出来る。 4級ァンモ -ゥム補足剤と しては活性炭、 ベントナイ ト、 キプロガム等が挙げられ、 排水中のホウフッ化水素酸除去後に、 これら を添加する事によって C O D, B O D値を抑えることが出来る。 Even if the borofluoride supplement of the present invention is added in a necessary amount or more, there is no problem in the ability to remove borofluoric acid, but the COD and BOD in the wastewater increase. It can be lost. In this case, by adding a quaternary ammonium scavenger after the borofluoric acid removal treatment, the surplus borofluoride scavenger can be removed. Activated carbon, bentonite, kipro gum and the like can be mentioned as quaternary gamma-pum supplements, and COD and BOD values can be suppressed by adding them after removing borofluoric acid in wastewater.
実施例  Example
本発明の一般式 ( 2 )、 一般式 (4 ) のホウフッ化捕捉剤について以 下の実施例に基き詳糸田に説明する。  The fluorinated fluorinated scavengers of the general formulas (2) and (4) of the present invention will be described in detail in Itoda based on the following examples.
〔実施例 1〕  (Example 1)
一般式 ( 2 )、 一般式 (4 ) で表される化合物として、 捕捉剤を以下 のように作成した。 1, 0 0 0 m 1 の水に 4級アンモニゥム塩又は置換 基によって 4級化された窒素を持つ含窒素複素環化合物を下記表 1に示 される量を溶解し、 にァェオン性高分子化合物を、 1, 0 0 O m l の 水に表 1に示される量を溶解し、 この 2つの水溶液を混合して生成した 沈殿物を採取してホゥフッ化水素酸捕捉剤を作成した。  As compounds represented by the general formulas (2) and (4), scavengers were prepared as follows. A quaternary ammonium salt or a nitrogen-containing heterocyclic compound having a nitrogen quaternized by a substituent is dissolved in 1,000 ml of water in an amount shown in Table 1 below, and the aeonionic polymer compound is dissolved in water. Was dissolved in 1,000 O ml of water in the amount shown in Table 1, and a precipitate formed by mixing the two aqueous solutions was collected to prepare a hydrofluoric acid scavenger.
【表 1 】 【table 1 】
5 001984 5 001984
17  17
Figure imgf000019_0001
アルギン酸 (君津化学株式会社製キミツアルギンサン)
Figure imgf000019_0001
Alginic acid (Kimitsu Chemical Co., Ltd. Kimitsu Arginsan)
ぺクチン (ドイツヘルプシュ トライ ト社製 L Mぺクチン)  Pectin (L M Pectin, German Helpstrite)
ゼラチン (新田ゼラチン株式会社製ゼラチン)  Gelatin (Gelatin manufactured by Nitta Gelatin Co., Ltd.)
ァユオン化でんぷん (日本澱粉株式会社製プリバイン p一 6 3 ) カルボシキメチルセルロース (第一工業製薬株式会社製セ口ゲン) ポリアク リル酸 (東亜合成株式会社製ァロン)  Ayuon starch (Privine p-163, manufactured by Nippon Starch Co., Ltd.) Carboxymethylcellulose (Daiichi Kogyo Seiyaku Co., Ltd. Seguchigen) Polyacrylic acid (Aron, manufactured by Toa Gosei Co., Ltd.)
アク リルアミ ドとアク リル酸との共重合体 (ラサフロ ック工業株式会 社製 R A— 5 1 )  Copolymer of acrylamide and acrylic acid (RA-51 from RasaFlok Industrial Co., Ltd.)
次に処理方法の実施例について詳細に説明する。  Next, an embodiment of the processing method will be described in detail.
処理水中のフッ素の分析は、 J i s K 0 1 0 2に定めるランタン ーァリザリ ンコ ンプレキソン法、 ホウ素の分析は同じく j I s K 0 1 0 2に定めるメチレンブルー吸光光度法により測定した。 処理方法の実施に試用した排水は、 メ ツキ工場から排出されたホウフ ッ化水素酸塩を含有するお 水を使用した。 The analysis of fluorine in the treated water was performed by the lanthanum-arizarin complexon method specified in JisK0102, and the analysis of boron was measured by the methylene blue absorption spectrophotometry specified in jIsK0102. The wastewater used for the treatment was water containing borohydride discharged from the Metzki plant.
この排水は、 ホウフッ化水素酸塩が 1 1 4 p p m ( l . 3 X 1 0— 3 m o 1 / 1 ; フッ素として 1 0 0 p p m、 ホウ素と して 1 4 p p m) 含 まれており、 p Hは 2. 8であった。 This waste water, fluoroboric acid salt 1 1 4 ppm; cage containing Marete (l 3 X 1 0- 3 mo 1/1. 1 4 ppm and fluorine as 1 0 0 ppm, boron), p H Was 2.8.
〔実施例 2〕  (Example 2)
排水 1, 0 0 ◦ m 1 に表 2に示すように一般式 ( 1 )、 一般式 ( 3 ) の化合物を添加して 5分間撹拌した後、 静置した。 このとき処理水には 白濁が見られたため、 更に 5 Aの濾紙で濾過した。 濾過液についてフッ 素、 ホウ素の分析を行った。 尚、 比較例と して一般式 ( 1 ) の化合物を 使用しないで同様の処理を行った。 その処理結果を表 2に示す。  As shown in Table 2, the compounds of the general formulas (1) and (3) were added to the wastewater at a temperature of 100 ° m 1, and the mixture was stirred for 5 minutes and then allowed to stand. At this time, the treated water was found to be cloudy, and was further filtered through a 5 A filter paper. The filtrate was analyzed for fluorine and boron. As a comparative example, the same treatment was performed without using the compound of the general formula (1). Table 2 shows the processing results.
【表 2】 [Table 2]
Figure imgf000020_0001
表 2に示す通り、 一般式 ( 1 ) 又は一般式 ( 3 ) の化合物を使用すれ ば、 排水中のフッ素とホウ素、 つまりホウフッ化水素酸塩の除去が可能 となる。 一般式 ( 1 ) 又は一般式 ( 3 ) の化合物の使用量をホウフッ化 水素酸塩と等モル以上とすれば、 5 p m程度まで除去が可能となる。
Figure imgf000020_0001
As shown in Table 2, the use of the compound of the general formula (1) or the general formula (3) makes it possible to remove fluorine and boron, that is, borofluoride, in wastewater. If the amount of the compound of the general formula (1) or (3) is equal to or more than that of the borofluoride, the compound can be removed up to about 5 pm.
〔実施例 3〕  (Example 3)
排水 1, 0 0 0 m 1 に一般式 ( 1 ) で表される化合物として、 トリメ チルステアリ ルアンモニゥムクロライ ドを 1 · 4 X 1 0一 3 m o 1 / 1 添加して 5分間撹拌した後、 凝集助剤と して珪藻土、 ベントナイ ト、 ァ ルギン酸ナトリ ゥムを矢々 1 gZ 1添加し、 更に水溶性高分子凝集剤と してアクリルアミ ドとアタ リル酸との共重合体 (ラサフロック工業株式 会社製 R A— 5 1 ) を添加して 5分間撹拌後、 静置した。 この時のスラ ッジの沈降速度 (上澄み液が澄明になるまでの時間) を目視により比較 した。 その結果を表 3に示す。 Trim as a compound represented by the general formula (1) After stirring Chirusuteari Ruan monitor © skeleton Lai de a 1 · 4 X 1 0 one 3 mo 1/1 added to 5 minutes, as a coalescing aid diatomaceous earth, bentonite DOO, arrows s 1 § alginic acid sodium © beam gZ1 was added, and a copolymer of acrylamide and acrylic acid (RA-51, manufactured by Rasafloc Industrial Co., Ltd.) was further added as a water-soluble polymer flocculant, and the mixture was stirred for 5 minutes and left to stand. . At this time, the sludge settling speed (the time until the supernatant liquid became clear) was visually compared. The results are shown in Table 3.
〔実施例 4〕  (Example 4)
排水 1 , 0 0 0 m l に一般式 ( 1 ) で表される化合物として、 トリメ チルステアリルアンモニゥムクロライ ド (表 3中 TMS AC) を 1. 4 X 1 0— 3m o 1 Z 1、 一般式 ( 3 ) で表される化合物と して、 セチル ピリ二ジゥムクロライ ド (表 3中 C P C) 1. 4 X 1 0— 3 m o 1 / 1 を夫々添加して 5分間撹拌、 凝集助剤と して珪藻土を 1 gZ 1添加して 5分間撹拌した後、 更に多価金属化合物と して塩化鉄、 希土類化合物と して硫酸セリ ウムを夫々 5 p p m添加した。 水溶性高分子凝集剤として アクリルアミ ドとアタリ ル酸との共重合体 (ラサフロック工業株式会社 製 RA— 5 1 ) を添加して 5分間撹拌後、 静置した。 この時のスラッジ の層厚を比較した。 その結果を表 3に示す。 Drainage 1, 0 0 as 0 ml in the general formula (1), the compound represented by the trimethyl chill stearyl ammonium Niu skeleton Rye de (in Table 3 TMS AC) 1. 4 X 1 0- 3 mo 1 Z 1, General and a compound represented by formula (3), stirred for 5 minutes cetyl two Jiumukurorai de (in Table 3 CPC) 1. 4 X 1 0- 3 mo 1/1 respectively were added, and the flocculating aid After adding 1 gZ1 of diatomaceous earth and stirring for 5 minutes, 5 ppm of iron chloride as a polyvalent metal compound and 5 ppm of cerium sulfate as a rare earth compound were added. As a water-soluble polymer coagulant, a copolymer of acrylamide and atarilic acid (RA-51, manufactured by Rasafloc Industrial Co., Ltd.) was added, and the mixture was stirred for 5 minutes and then allowed to stand. The sludge layer thickness at this time was compared. The results are shown in Table 3.
スラッジの層厚: 処理工程終了 1 0分後のスラッジの厚さを目視で確 認した。 (スラッジの厚さノ排水の液までの高さ) で割合を記載。  Sludge layer thickness: The thickness of the sludge 10 minutes after the completion of the treatment step was visually checked. (Thickness of sludge and height of liquid to drainage) The ratio is described.
【表 3】 一般式 [1]/[3] 凝集助剤 多価金属/希土類 沈降速度 スラッジの層厚 本発明 2 T SAC ― ― 沈降しない 一 本発明 10 T SAC 珪藻土 一 30秒 0.10 本発明 11. TMSAC ベントナイト 一 50秒 0.12 本発明 12 TMSAC アルギン酸ナトリウム -一 60秒 0.12 本発明 13 TMSAC 珪藻土 塩化鉄 20秒 0.06 本発明 14 TMSAC 珪藻七 硫酸セリウム 20秒 0.05 本発明 15 CPC 珪藻土 一 35秒 0.11 本発明 ]6 CPC ベントナイト 一 50秒 0.12 本癸明 17 CPC アルギン酸ナトリウム 一 65秒 0.12 本発明 18 CPC 珪藻土 塩化鉄 25秒 0.05 本発明 19 CPC 珪藻土 硫酸セリウム 20秒 0.06[Table 3] General formula [1] / [3] Coagulation aid Polyvalent metal / rare earth Sedimentation velocity Sludge layer thickness Invention 2 T SAC--No sedimentation 1 Invention 10 T SAC diatomaceous earth 30 seconds 0.10 Invention 11 TMSAC bentonite 1 50 seconds 0.12 Invention 12 TMSAC sodium alginate-60 seconds 0.12 Invention 13 TMSAC diatomaceous earth chloride 20 seconds 0.06 Invention 14 TMSAC diatom cerium sulphate 20 seconds 0.05 Invention 15 CPC diatomaceous earth 35 seconds 0.11 Invention] 6 CPC bentonite One 50 seconds 0.12 Higashiki 17 CPC sodium alginate One 65 seconds 0.12 Invention 18 CPC diatomaceous earth iron chloride 25 seconds 0.05 Invention 19 CPC diatomaceous earth cerium sulfate 20 seconds 0.06
※なお本発明 10~14における処理結果は全て、フッ素濃度は 5ppm以下、ホウ素濃度は lppm以下であった。 尚、 本発明 1 0〜 1 4に於ける処理結果は全て、 フッ素濃度は 5 p p m以下、 ホウ素濃度は 1 P PM以下であった。 * In all of the treatment results of the present inventions 10 to 14, the fluorine concentration was 5 ppm or less and the boron concentration was 1 ppm or less. In all of the processing results in the present invention, the fluorine concentration was 5 ppm or less and the boron concentration was 1 ppm or less.
表 3に示す通り、 凝集助剤を使用することでホウフッ化水素酸塩と一 般式 ( 1 ) 又は一般式 ( 3 ) で表される化合物で生成する難溶性物質を 速やかに凝集 · 沈降することが可能となる。 更に多価金属類 Z希土類化 合物を併用することにより沈降速度を速め、 スラッジ量を減容すること が可能となる。  As shown in Table 3, the use of the flocculation aid quickly flocculates and precipitates the poorly soluble substance formed by the borofluoride and the compound represented by the general formula (1) or (3). It becomes possible. Further, by using a polyvalent metal Z rare earth compound in combination, it is possible to increase the sedimentation speed and reduce the amount of sludge.
〔実施例 5〕  (Example 5)
一般式 ( 2) で表される化合物と して、 トリメチルステアリルアンモ -ゥムクロライ ドを 3 5 gを 1 , 0 0 0 m l の水に溶解し、 更にァニォ ン性高分子化合物と してキミツアルギン 2 0 gを 1, 0 0 0 m l の水に 溶解し、 この 2つの水溶液を混合して生成した沈殿物を採取してホウフ ッ化水素酸捕捉剤 1、 1 5を作成した。  As a compound represented by the general formula (2), 35 g of trimethylstearylammonium-pum chloride is dissolved in 1,000 ml of water, and Kimizargin 20 is dissolved as an anionic polymer compound. g was dissolved in 1,000 ml of water, and the two aqueous solutions were mixed, and the resulting precipitate was collected to prepare borofluoric acid scavengers 1,15.
排水 1, 0 0 0 m 1 にホウフッ化水素酸捕捉剤 1を表 4に示す通り添 加して、 1時間撹拌後、 固液分離を行い、 フッ素濃度、 ホウ素濃度の測 定を行った。 比較例として、 排水の: Hを N a O Hで、 7. 5に夫々調 整して同様の操作を行った。 その結果を表 4に示す。  Boron hydrofluoric acid scavenger 1 was added to 1,000 ml of wastewater as shown in Table 4, and after stirring for 1 hour, solid-liquid separation was performed, and the fluorine and boron concentrations were measured. As a comparative example, the same operation was performed by adjusting the H of the waste water to 7.5 with NaOH. The results are shown in Table 4.
【表 4】 捕捉剤 1の使用量 水の pH 処理後のフッ素濃度 処理後のホウ素濃度 比較例 2 5.0g 1排水 1L 7.0 97.5 ppm 13.8ppm 比較例 3 10-Og 1排水 1L 7.0 97.8 ppm 14.0 ppm 比較例 4 20.0g /排水 1し 7.0 99.0 ppm 13.8 ppm 比較例 5 5.0g 1排水 1L 5.0 98.0 ppm 13.0 ppm 比較例 6 lO.Og /排水 1L 5.0 97.5 ppm 14.0 ppm 比較例 7 20.0g 1排水 1L 5.0 97.0 ppm 13.6 ppm 実施例 20 2.5g 1排水 1L 2.8 35.0 ppm 5.0 ppm 実施例 21 5.0g 1排水 1L 2.8 9.2 ppm 0.8 ppm 実施例 22 l O.Og /排水 1L 2.8 1.5 ppm 0.1 ppm 表 4に示す通り、 被処理水の : p Hが 5以上の場合には、 ホウフッ化水 素酸塩の除去はできないが、 p Hが 5未満であれば、 該捕捉剤を使用す ることでホウフッ化水素酸塩を除去することができる。 [Table 4] Amount of scavenger 1 Fluorine concentration after water pH treatment Boron concentration after treatment Comparative Example 2 5.0 g 1 Wastewater 1 L 7.0 97.5 ppm 13.8 ppm Comparative Example 3 10-Og 1 Wastewater 1 L 7.0 97.8 ppm 14.0 ppm Comparative Example 4 20.0 g / drain 1 7.0 99.0 ppm 13.8 ppm Comparative 5 5.0 g 1 drain 1 L 5.0 98.0 ppm 13.0 ppm Comparative 6 lO.Og / drain 1 L 5.0 97.5 ppm 14.0 ppm Comparative 7 20.0 g 1 drain 1 L 5.0 97.0 ppm 13.6 ppm Example 20 2.5 g 1 Wastewater 1 L 2.8 35.0 ppm 5.0 ppm Example 21 5.0 g 1 Wastewater 1 L 2.8 9.2 ppm 0.8 ppm Example 22 l O.Og / Wastewater 1 L 2.8 1.5 ppm 0.1 ppm Treated water as shown in Table 4 : If the pH is 5 or more, borofluoride cannot be removed, but if the pH is less than 5, use the scavenger to remove borofluoride be able to.
同様に、 その他の捕捉剤 2〜 1 4を使用してメ ツキ工場排水の処理を 行った。 メツキ工場排水の; p Hは 2 . 8、 捕捉剤の使用量はすべて 1 0 g Z排水 1 1 として処理を行い、 フッ素濃度、 ホウ素濃度の測定を行つ た。 その結果を表 5に示す。  Similarly, the treatment of effluent from the sapphire factory was carried out using other scavengers 2 to 14. The pH of the wastewater from the Metsuki Plant was 2.8, and the amount of trapping agent used was all 10 g. The wastewater was treated as 11 and the fluorine and boron concentrations were measured. Table 5 shows the results.
【表 5】 [Table 5]
処理後のフッ素濃度 処理後のホウ素濃度 実施例 23 捕捉剤 2 2.0 ppm 0.2 ppm Fluorine concentration after treatment Boron concentration after treatment Example 23 Scavenger 2 2.0 ppm 0.2 ppm
実施例 24 捕捉剤 3 1.8 ppm 0.2 ppm  Example 24 Scavenger 3 1.8 ppm 0.2 ppm
実施例 25 捕捉剤 4 1.6 ppm 0.1 ppm  Example 25 Scavenger 4 1.6 ppm 0.1 ppm
実施例 26 捕捉剤 5 2.1 ppm 0.2 ppm  Example 26 Scavenger 5 2.1 ppm 0.2 ppm
実施例 27 捕捉剤 6 l.o ppm 0.1 ppm  Example 27 Capture agent 6 l.o ppm 0.1 ppm
実施例 28 捕捉剤 7 1.6 ppm 0.1 pm  Example 28 Scavenger 7 1.6 ppm 0.1 pm
実施例 29 捕捉剤 8 2.2 ppm 0.3 ppm  Example 29 Scavenger 8 2.2 ppm 0.3 ppm
実施例 30 捕捉剤 9 1.5 ppm 0.2 ppm  Example 30 Scavenger 9 1.5 ppm 0.2 ppm
実施例 31 捕捉剤 10 1.4 ppm 0.3 ppm  Example 31 Scavenger 10 1.4 ppm 0.3 ppm
実施例 32 捕捉剤 11 2.1 ppm 0.1 pm  Example 32 Scavenger 11 2.1 ppm 0.1 pm
実施例 33 捕捉剤 12 1.3 ppm 0.3 ppm  Example 33 Scavenger 12 1.3 ppm 0.3 ppm
実施例 34 捕捉剤 13 1.8 ppm 0.2 ppm  Example 34 Scavenger 13 1.8 ppm 0.2 ppm
実施例 35 捕捉剤 14 1.5 ppm 0.2 ppm  Example 35 Scavenger 14 1.5 ppm 0.2 ppm
実施例 36 捕捉剤 15 2.5 ppm 0.3 ppm  Example 36 Scavenger 15 2.5 ppm 0.3 ppm
実施例 37 捕捉剤 16 1.4 ppm 0.3 ppm  Example 37 Capture agent 16 1.4 ppm 0.3 ppm
実施例 38 捕捉剤 17 1.4 ppm 0.1 ppm  Example 38 Scavenger 17 1.4 ppm 0.1 ppm
実施例 39 捕捉剤 18 2.3 ppm 0.1 ppm  Example 39 Scavenger 18 2.3 ppm 0.1 ppm
実施例 40 捕捉剤 19 1.5 ppm 0.3 ppm  Example 40 Scavenger 19 1.5 ppm 0.3 ppm
実施例 41 捕捉剤 20 1.6 ppm 0.2 ppm  Example 41 Scavenger 20 1.6 ppm 0.2 ppm
実施例 42 捕捉剤 21 2.0 ppm 0.3 ppm 表 5に示す通り、 すべての捕捉剤でホウフッ化水素酸塩を除去するこ とができる。  Example 42 Scavenger 21 2.0 ppm 0.3 ppm As shown in Table 5, all scavengers can remove borofluoride.
〔実施例 6〕  (Example 6)
ホウフッ化水素酸捕捉剤 1を充填槽に 5 0 0 g充填して、 ここに毎分 1, 0 0 0 m 1 のお 水を通水した。 1 0 0 1 処理する毎に得られた処理 水のフッ素濃度、 ホウ素濃度の測定を行った。 その結果を表 6に示す。 【表 6】 排水通水量 フッ素濃度 処理後のホウ素濃度500 g of borofluoric acid scavenger 1 was filled in a filling tank, and water of 1,000 m 1 per minute was passed therethrough. The fluorine concentration and the boron concentration of the treated water obtained each time the treatment was performed were measured. Table 6 shows the results. [Table 6] Wastewater flow rate Fluorine concentration Boron concentration after treatment
100L 2.2 ppm 0,2 ppm 100L 2.2 ppm 0.2 ppm
200L 2.5 ppm 0.3 ppm  200L 2.5 ppm 0.3 ppm
300L 3,8 ρρτη 0.3 ppm  300L 3,8 ρρτη 0.3 ppm
400L 4.2 ppm 0.5 ppm  400L 4.2 ppm 0.5 ppm
500L 4.8 ppm 0.6 ppm  500L 4.8 ppm 0.6 ppm
600L 6.8 ppm 1.1 ppm  600L 6.8 ppm 1.1 ppm
700L 16.0 ppm 2,0 ppm 表 6に示す通り、 ホウフッ化水素酸捕捉剤中に通水することにより、 ホウフッ化水素酸塩を除去することができる。 然し、 処理水の量が一定 の値を超えると除去率が低下する。  700L 16.0 ppm 2,0 ppm As shown in Table 6, the water can be passed through the borofluoric acid scavenger to remove borofluoride. However, when the amount of treated water exceeds a certain value, the removal rate decreases.
次に、 ホウフッ化水素酸捕捉剤の再生方法について詳細に説明する。 〔実施例 7〕  Next, a method for regenerating the borofluoric acid scavenger will be described in detail. (Example 7)
実施例 6で 7 0 0 1の排水を処理した後、 充填槽に p H 1 0に調整し た N a H O溶液を満たした。 3 0分後、 N a O H溶液を廃棄した後、 水 で洗浄し再生を行った。 再度この充填槽を使用して実施例 5に従い排水 の処理を行った。 その結果を表 7に示す。  After treating the wastewater of 7001 in Example 6, the filling tank was filled with a NaHO solution adjusted to pH10. After 30 minutes, the NaOH solution was discarded, washed with water and regenerated. The wastewater was treated according to Example 5 again using this filling tank. Table 7 shows the results.
【表 7】  [Table 7]
Figure imgf000025_0001
表 7に示すように、 一度ホウフッ化水素酸塩の除去に使用したホウフ ッ化水素酸捕捉剤をアル力 リ溶液中で処理することにより、 再度使用す ることが可能になった。
Figure imgf000025_0001
As shown in Table 7, the borofluoric acid scavenger once used to remove the borofluoride was reused by treating it in an alkaline solution. It became possible to do.
〔実施例 8〕  (Example 8)
フッ素として 1 0 g /L のホウフッ化物含有排水 1 0 0 0 ml に塩化 力リ ゥムを添加して反応後、 ホウフッ化力リ ウムと して析出した沈殿物 を除去した液に一般式 ( 1 ) で表される化合物と して、 ト リ メチルステ ァリルアンモ-ゥムク口ライ ドを、 一般式 ( 3 ) で表される化合物と し て、 セチルピリジゥムクロライ ドを各々添加して 5分間攪拌、 凝集助剤 と して珪藻土 1 g /L添力 Bして 5分間攪拌した後、 水溶性高分子凝集剤 と してアクリルアミ ドとァク リル酸との共重合体 (ラサフロ ック工業株 式会社製 R A -51) を添加して 5分間攪拌後、 静置した。 上澄み中のフ ッ素濃度を測定した結果、 フッ素は 8 p p m以下となった。 その結果を 表 8に示す。  After adding 100 ml of waste water containing 100 g / L of borofluoride as fluorine and reacting with 100 ml of fluorinated water, the liquid obtained by removing the precipitate deposited as borofluoridium has the general formula ( 1) Trimethyl stearylammonium chloride is added as the compound represented by (1), and cetyl pyridium chloride is added as the compound represented by the general formula (3), and the mixture is stirred for 5 minutes. Diatomaceous earth 1 g / L as coagulant Aid B, stirred for 5 minutes, then copolymerized with acrylamide and acrylic acid as water-soluble polymer coagulant (RasaFlok Industries, Ltd.) RA-51) manufactured by Co., Ltd. was added, and the mixture was stirred for 5 minutes and then allowed to stand. As a result of measuring the fluorine concentration in the supernatant, the fluorine content was less than 8 ppm. Table 8 shows the results.
【表 8】  [Table 8]
Figure imgf000026_0001
Figure imgf000026_0001
表 8に示すよ うに、 多量のホウフッ化物を含む廃液の場合、 本発明 4 3、 4 6では多量のホウフッ化水素酸補足剤を添加する必要があるが、 本発明 4 5、 4 8では予め塩化カリ ウムである程度除去出来る為、 ホウ フッ化水素酸補足剤は少量で充分に除去効果を出す事が出来た。  As shown in Table 8, in the case of a waste liquid containing a large amount of borofluoride, it is necessary to add a large amount of a hydrofluoric acid scavenger in the present inventions 43 and 46. Since it can be removed to some extent with potassium chloride, a small amount of borofluoric acid scavenger was able to achieve a sufficient removal effect.
〔実施例 9〕  (Example 9)
排水 1 0 0 O ml に一般式 ( 1 ) で表される化合物と して、 ト リ メチ ルステアリルァンモニゥムク口ライ ドを 1 . 4 X 1 0 一 3 m o 1 ZL添加 して 5分攪拌、 凝集助剤と して珪藻土 1 g /L添加して 5分間攪拌した 後、 水溶性高分子凝集剤と してァクリルアミ ドとァクリル酸との共重合 体 (ラサフロ ッ ク工業株式会社製 R A -51) を添加して 5分間攪拌後、 固液分離した。 濾液に 4級アンモユウム捕捉剤と して活性炭、 ベントナ イ ト、 キプロガムを各々添加し 5分攪拌後、 固液分離した液の C O Dを 比較した。 その結果を表 9に示す。 Trimethylene is added to 100 mL of wastewater as a compound represented by the general formula (1). 1 Le stearyl § emissions monitor © Solid opening line de. 4 X 1 0 one 3 mo 1 ZL added to 5 minutes stirring, after as a coalescing aid stirring kieselguhr 1 g / L added to 5 minutes, water A copolymer of acrylamide and acrylic acid (RA-51, manufactured by RasaFlok Industries Co., Ltd.) was added as a conductive polymer flocculant, and the mixture was stirred for 5 minutes, and then subjected to solid-liquid separation. Activated carbon, bentonite, and kipro gum were added to the filtrate as quaternary ammonium scavengers, and after stirring for 5 minutes, the COD of the solid-liquid separated liquid was compared. Table 9 shows the results.
【表 9】 [Table 9]
Figure imgf000027_0001
Figure imgf000027_0001
表 9に示すよ うに、 ホウフッ化水素酸補足剤が余剰になった場合、 排 液処理後の C O Dは上がってしまうが、 4級アンモユウム捕足剤を添加 する事によって、 余剰分のホウフッ化水素酸補足剤を除去する事が出来 た。 産業上の利用可能性  As shown in Table 9, if the borofluoric acid scavenger becomes excessive, the COD after drainage increases, but the addition of the quaternary ammonium scavenger results in an excess of borofluoric acid. The acid scavenger could be removed. Industrial applicability
以上のように、 本発明にかかるホウフッ化水素酸塩を含有する排水の 処理方法に使用する添加剤及ぴその処理方法は、 ホウフッ化水素酸塩を 含有する排水から、 加熱等の外部エネルギーを使用することなく、 少な ぃスラッジ量で短時間にフッ素及ぴホウ素を除去することができるので 有用である。 更に、 2次処理 (高度処理) のための槽を設置する等設備 の増強の必要がな く、 既存の 1次処理設備のみで高度処理が可能となる ので有用である。 As described above, the additive used in the method for treating effluent containing borofluoride according to the present invention and the method for treating the effluent contain external energy such as heating from the effluent containing borofluoride. This is useful because fluorine and boron can be removed in a short time with a small amount of sludge without using it. In addition, facilities such as installing tanks for secondary processing (advanced processing) This is useful because it does not need to be increased and advanced treatment can be performed only with the existing primary treatment equipment.

Claims

請 求 の 範 囲 The scope of the claims
1. 排水からホウフッ化水素酸を除去する添加剤で、 下記一般式 ( 1 ) 〜 (4) で表される化合物の少なく とも 1種よりなることを特徴とする ホウフッ化水素酸捕捉剤。 1. An additive for removing borofluoric acid from wastewater, comprising at least one compound represented by the following general formulas (1) to (4).
一般式 ( 1 )  General formula (1)
Figure imgf000029_0001
Figure imgf000029_0001
R i〜R 4は夫々独立に炭素数 1〜 2 4のアルキル基、 ァルケ-ル基、 フエニル基又はベンジル基を表し、 R i〜R 4が互いに連結して環を形 成してもよい。 X は陰イオンを表す。 R i to R 4 each independently represent an alkyl group having 1 to 24 carbon atoms, an alkyl group, a phenyl group or a benzyl group, and R i to R 4 may be linked to each other to form a ring; . X represents an anion.
一般式 ( 2 )  General formula (2)
Figure imgf000029_0002
Figure imgf000029_0002
R 〜R 4は夫々独立に炭素数 1〜 24のアルキル基、 アルケニル基、 フエニル基又はベンジル基を表し、 R 〜R 4が互いに連結して環を形 成してもよい。 Aはァニオン性高分子を表す。 R 4 to R 4 each independently represent an alkyl group, alkenyl group, phenyl group or benzyl group having 1 to 24 carbon atoms, and R 4 to R 4 may be linked to each other to form a ring. A represents an anionic polymer.
一般式 ( 3 ) ^ ノ General formula (3) ^ ノ
C '  C '
R iは炭素数 1〜 2 4のァノレキル基、 アルケニル基、 フエニル基又は ベンジル基を表す。 Zはへテロ環を構成するのに必要な原子群を表す。 X一は陰イオンを表す。 R i represents an anoalkyl group having 1 to 24 carbon atoms, an alkenyl group, a phenyl group or a benzyl group. Z represents an atomic group necessary for constituting a hetero ring. X represents an anion.
一般式 (4)  General formula (4)
Ri ""- +N Z
Figure imgf000030_0001
A
Ri ""- + NZ
Figure imgf000030_0001
A
R iは炭素数 1〜 2 4のアルキル基、 ァルケ-ル基、 フエ二ゾレ基又は ベンジル基を表す。 Zはへテロ環を構成するのに必要な原子群を表す。 Aはァェオン性高分子を表す。 R i represents an alkyl group having 1 to 24 carbon atoms, an alkyl group, a phenylazole group or a benzyl group. Z represents an atomic group necessary for constituting a hetero ring. A represents an aeon polymer.
2. —般式 ( 2) 及び一般式 (4) で表されるホウフッ化水素酸捕捉 斉 IJの Aが下記の A群から選ばれる構造を有することを特徴とする請求項 2. —A compound of the formula (2) and formula (4), wherein A of the borofluoric acid trapping complex IJ has a structure selected from the following group A:
1 に記載のホウフッ化水素酸捕捉剤。 2. The borofluoric acid scavenger according to 1.
A群 : アルギン酸、 ぺクチン、 ゼラチン、 ァニオン化でんぷん、 カル ポキシメチルセルロース、 ポリアクリル酸、 アク リルアミ ドとアクリル 酸との共重合体  Group A: Alginate, pectin, gelatin, anionized starch, carboxymethylcellulose, polyacrylic acid, copolymer of acrylic acid and acrylic acid
3. 4級アンモニゥム塩 1モルに対し、 ァニオン性高分子のァニオン 十生部位のモル数が 0. 0 1〜 5. 0モルの割合で作成されたことを特徴 とする請求項 2に記載のホウフッ化水素酸捕捉剤。  3. The method according to claim 2, wherein the number of moles of the anionic polymer site is 0.01 to 5.0 moles per mole of the quaternary ammonium salt. Borofluoric acid scavenger.
4. ホウフッ化水素酸塩を含有する排水からホウフッ化水素酸を除去 する排水処理方法に関し、 該排水へ下記一般式 ( 1 ) 又は一般式 ( 3 ) で表されるホウフッ化水素酸捕捉剤の少なく とも 1種を添加することを 特徴とする排水処理方法。 4. Regarding a wastewater treatment method for removing borofluoric acid from wastewater containing borofluoride, the following general formula (1) or general formula (3) is added to the wastewater. A wastewater treatment method comprising adding at least one kind of a borofluoric acid scavenger represented by the formula:
一般式 ( 1 )  General formula (1)
Figure imgf000031_0001
R i〜R 4は夫々独立に炭素数 1〜 2 4のアルキル基、アルケニル基、 フエ-ル基又はベンジル基を表し、 R i〜R 4が互いに連結して環を形 成してもよい。 X—は陰イオンを表す。
Figure imgf000031_0001
R i to R 4 each independently represent an alkyl group, alkenyl group, phenyl group or benzyl group having 1 to 24 carbon atoms, and R i to R 4 may be linked to each other to form a ring; . X— represents an anion.
一般式 ( 3 ) z 、  General formula (3) z,
C ' R iは炭素数 1〜 2 4のアルキル基、 アルケュル基、 フエ-ル基又は ベンジル基を表す。 Zはへテロ環を構成するのに必要な原子群を表す。 C ′ Ri represents an alkyl group having 1 to 24 carbon atoms, an alkyl group, a fuel group or a benzyl group. Z represents an atomic group necessary for constituting a hetero ring.
X -は陰イオンを表す。 X- represents an anion.
5. 排水中に含まれるホウフッ化水素酸イオン 1モル当たり 0. 1〜 0. 5モルの下記一般式 ( 1 ) で表されるホウフッ化水素酸捕捉剤を添 加することを特徴とする請求項 4に記載の排水処理方法。  5. A method comprising adding 0.1 to 0.5 mol of a borofluoric acid scavenger represented by the following general formula (1) per 1 mol of borofluoric acid ions contained in wastewater. Item 4. The wastewater treatment method according to Item 4.
一般式 ( 1 )  General formula (1)
Figure imgf000031_0002
R 〜 4は夫々独立に炭素数 1〜 2 4のアルキル基、ァルケエル基、 フエニル基又はベンジル基を表し、 R i〜R 4が互いに連結して環を形 成してもよい。 X は陰イオンを表す。
Figure imgf000031_0002
R to R 4 each independently represent an alkyl group having 1 to 24 carbon atoms, a alkenyl group, a phenyl group or a benzyl group, and Ri to R 4 may be linked to each other to form a ring. X represents an anion.
6 . 一般式 ( 1 ) 又は一般式 ( 3 ) で表されるホウフッ化水素酸捕捉 剤の少なく とも 1種を添加した後、 珪藻土、 ベントナイ ト、 カオリン、 活性炭、 ポルトラン ドセメ ン ト、 親水性高分子化合物、 多価金属類、 希 土類化合物から選択される 1種以上の化合物を添加することを特徴とす る請求項 4又は 5に記載の排水処理方法。  6. After adding at least one of the borofluoric acid scavengers represented by the general formula (1) or (3), diatomaceous earth, bentonite, kaolin, activated carbon, portland cement, high hydrophilicity, etc. The wastewater treatment method according to claim 4, wherein one or more compounds selected from a molecular compound, a polyvalent metal, and a rare earth compound are added.
7 . 該化合物の添加量は被処理水の 0 . 0 0 0 5〜 5 . 0重量。/。であ ることを特徴とする請求項 6に記載の排水処理方法。  7. The amount of the compound to be added is 0.0005 to 5.0% by weight of the water to be treated. /. The wastewater treatment method according to claim 6, wherein:
8 . ホウフッ化水素酸塩を含有する排水と、 一般式 ( 2 ) 又は一般式 ( 4 ) で表されるホウフッ化水素酸捕捉剤を p H 5未満で接触させるこ とを特徴とする排水処理方法。  8. Wastewater treatment characterized by contacting wastewater containing borofluoride with a borofluoric acid scavenger represented by the general formula (2) or (4) at a pH of less than 5. Method.
一般式 ( 2 )  General formula (2)
Figure imgf000032_0001
Figure imgf000032_0001
R 〜R 4は夫々独立に炭素数 1〜 2 4のアルキル基、アルケニル基、 フェュル基又はベンジル基を表し、 R 〜R 4が互いに連結して環を形 成してもよい。 Aは下記 A群から選ばれるァユオン性高分子を表す。 R to R 4 each independently represent an alkyl group, alkenyl group, phenyl group or benzyl group having 1 to 24 carbon atoms, and R to R 4 may be linked to each other to form a ring. A represents an ayuonic polymer selected from Group A below.
A群 : アルギン酸、 ぺクチン、 ゼラチン、 ァニオン化でんぷん、 カル ボキシメチルセノレロ ース、 ポリアタリノレ酸、 アタ リノレア ミ ドとアタリノレ 酸との共重合体  Group A: Alginic acid, pectin, gelatin, anionized starch, carboxymethyl senorellose, polyatalinoleic acid, copolymer of atalinoleamide and atalinoleic acid
一般式 (4 ) Ri— N Z A General formula (4) Ri—NZA
 No
R iは炭素数 1〜 2 4のアルキル基、 ァルケエル基、 フエ-ル基又は ベンジル基を表す。 Zはへテロ環を構成するのに必要な原子群を表す。  R i represents an alkyl group having 1 to 24 carbon atoms, an alkyl group, a fuel group or a benzyl group. Z represents an atomic group necessary for constituting a hetero ring.
はァ RRNII  Haa RRNII
A ユオン性高分子を表す卜 23。 A represents a union polymer.
9. 下記一般式 ( 2) 又は一般式 (4) で表されるホウフッ化水素酸 捕捉剤の再生方法に関し、 ホウフッ化水素酸を捕捉した捕捉剤を!) H 8 以上に調整した水溶液と接触させることで再生することを特徴とするホ ゥフッ化水素酸捕捉剤の再生方法。  9. Regarding the method for regenerating the borofluoric acid capturing agent represented by the following general formula (2) or (4), use a capturing agent that captures borofluoric acid! A method for regenerating a hydrofluoric acid scavenger, comprising regenerating by contacting with an aqueous solution adjusted to H 8 or more.
一般式 ( 2)  General formula (2)
one
Figure imgf000033_0001
Figure imgf000033_0001
1 1〜1 4は夫々独立に炭素数 1〜2 4のアルキル基、 ァルケ-ル基、 フエニル基又はベンジル基を表し、 R i R が互いに連結して環を形 成してもよい。 Aはァ-オン性高分子を表す。 1 1 to 1 4 are each independently of the number 1-2 4 alkyl carbon, Aruke - group, represents a phenyl group or a benzyl group, the ring may form a form a linked R i R each other. A represents an ionic polymer.
一般式 (4)  General formula (4)
Figure imgf000033_0002
Figure imgf000033_0002
R丄は炭素数 1〜 2 4のアルキル基、 アルケニル基、 フエニル基又は ベンジル基を表す。 zはへテロ環を構成するのに必要な原子群を表す。 Aはァ オン性高分子を表す。 R represents an alkyl group having 1 to 24 carbon atoms, an alkenyl group, a phenyl group or a benzyl group. z represents an atomic group necessary for constituting a hetero ring. A represents an aionic polymer.
要 約 書 メ ツキ加工業者、 ガラス加工業者、 プリ ント基板加工業者等が排出す るホウフッ化水素酸塩を含有する排水の処理を従来装置を使用して極め て簡単に且つ効率よくスラッジの発生を抑えて常温で短時間に処理でき るようにする。 The use of conventional equipment for the treatment of wastewater containing borofluoride discharged by metalworkers, glass processors, print substrate processors, etc. makes it extremely easy and efficient to generate sludge. So that processing can be performed at room temperature in a short time.
その課題を解決する手段は、 下記一般式 ( 1 ) 又は ( 2 ) で表される ホウフッ化水素酸捕捉剤である。  Means for solving the problem is a borofluoric acid scavenger represented by the following general formula (1) or (2).
一般式 ( 1 )  General formula (1)
R ル基、 フエ 環を形 成し R group to form a Hue ring
 One
Figure imgf000035_0001
Figure imgf000035_0001
R i〜R 4は夫々独立に炭素数 1〜 2 4のアルキル基、 アルケニル基、 フエニル基又はベンジル基を表し、 R i〜R 4が互いに連結して環を形 成してもよい。 Aはァニオン性高分子を表す。 R i to R 4 each independently represent an alkyl group, alkenyl group, phenyl group or benzyl group having 1 to 24 carbon atoms, and R i to R 4 may be linked to each other to form a ring. A represents an anionic polymer.
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JPH03119189A (en) * 1989-10-03 1991-05-21 Nippon Kamiparupu Kenkyusho:Kk Treatment of white liquor of paper mill
JPH07195085A (en) * 1994-01-12 1995-08-01 Electric Power Dev Co Ltd Treatment of dithionic acid ion-containing water

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JP2005224670A (en) * 2004-02-10 2005-08-25 Chugai Photo Chemical Co Ltd Method for treating fluorine-containing waste water
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