JPS5918111B2 - Water treatment method - Google Patents
Water treatment methodInfo
- Publication number
- JPS5918111B2 JPS5918111B2 JP12454076A JP12454076A JPS5918111B2 JP S5918111 B2 JPS5918111 B2 JP S5918111B2 JP 12454076 A JP12454076 A JP 12454076A JP 12454076 A JP12454076 A JP 12454076A JP S5918111 B2 JPS5918111 B2 JP S5918111B2
- Authority
- JP
- Japan
- Prior art keywords
- water
- treatment
- tower
- cartridge
- treated
- 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
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims description 60
- 238000000034 method Methods 0.000 title claims description 37
- 238000001179 sorption measurement Methods 0.000 claims description 24
- 230000008569 process Effects 0.000 claims description 22
- 239000003463 adsorbent Substances 0.000 claims description 18
- 238000009287 sand filtration Methods 0.000 claims description 12
- 239000000126 substance Substances 0.000 claims description 12
- 230000037081 physical activity Effects 0.000 claims 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 23
- 239000004576 sand Substances 0.000 description 22
- 239000003921 oil Substances 0.000 description 21
- 239000002351 wastewater Substances 0.000 description 21
- 239000000463 material Substances 0.000 description 18
- -1 ester derivatives of acrylic acid Chemical class 0.000 description 16
- 238000012545 processing Methods 0.000 description 14
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 12
- 239000000835 fiber Substances 0.000 description 12
- 229920001155 polypropylene Polymers 0.000 description 10
- 239000004743 Polypropylene Substances 0.000 description 9
- 239000000839 emulsion Substances 0.000 description 9
- 238000001914 filtration Methods 0.000 description 9
- RHZUVFJBSILHOK-UHFFFAOYSA-N anthracen-1-ylmethanolate Chemical compound C1=CC=C2C=C3C(C[O-])=CC=CC3=CC2=C1 RHZUVFJBSILHOK-UHFFFAOYSA-N 0.000 description 7
- 239000003365 glass fiber Substances 0.000 description 7
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- 238000007789 sealing Methods 0.000 description 5
- 229910000831 Steel Inorganic materials 0.000 description 4
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 4
- 239000000945 filler Substances 0.000 description 4
- VTHJTEIRLNZDEV-UHFFFAOYSA-L magnesium dihydroxide Chemical compound [OH-].[OH-].[Mg+2] VTHJTEIRLNZDEV-UHFFFAOYSA-L 0.000 description 4
- 239000000347 magnesium hydroxide Substances 0.000 description 4
- 229910001862 magnesium hydroxide Inorganic materials 0.000 description 4
- 238000004519 manufacturing process Methods 0.000 description 4
- 229920000642 polymer Polymers 0.000 description 4
- 239000010959 steel Substances 0.000 description 4
- ZCYVEMRRCGMTRW-UHFFFAOYSA-N 7553-56-2 Chemical compound [I] ZCYVEMRRCGMTRW-UHFFFAOYSA-N 0.000 description 3
- YMWUJEATGCHHMB-UHFFFAOYSA-N Dichloromethane Chemical compound ClCCl YMWUJEATGCHHMB-UHFFFAOYSA-N 0.000 description 3
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- 229910052740 iodine Inorganic materials 0.000 description 3
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- 238000012423 maintenance Methods 0.000 description 3
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- NWUYHJFMYQTDRP-UHFFFAOYSA-N 1,2-bis(ethenyl)benzene;1-ethenyl-2-ethylbenzene;styrene Chemical compound C=CC1=CC=CC=C1.CCC1=CC=CC=C1C=C.C=CC1=CC=CC=C1C=C NWUYHJFMYQTDRP-UHFFFAOYSA-N 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- KAKZBPTYRLMSJV-UHFFFAOYSA-N Butadiene Chemical compound C=CC=C KAKZBPTYRLMSJV-UHFFFAOYSA-N 0.000 description 2
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 2
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- CERQOIWHTDAKMF-UHFFFAOYSA-N Methacrylic acid Chemical compound CC(=C)C(O)=O CERQOIWHTDAKMF-UHFFFAOYSA-N 0.000 description 2
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 description 2
- 239000004793 Polystyrene Substances 0.000 description 2
- PPBRXRYQALVLMV-UHFFFAOYSA-N Styrene Chemical compound C=CC1=CC=CC=C1 PPBRXRYQALVLMV-UHFFFAOYSA-N 0.000 description 2
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- 208000016468 chronic pneumonitis of infancy Diseases 0.000 description 2
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- 229920001577 copolymer Polymers 0.000 description 2
- 229910052802 copper Inorganic materials 0.000 description 2
- 239000010949 copper Substances 0.000 description 2
- 229910001873 dinitrogen Inorganic materials 0.000 description 2
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- 239000011521 glass Substances 0.000 description 2
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- SMZOUWXMTYCWNB-UHFFFAOYSA-N 2-(2-methoxy-5-methylphenyl)ethanamine Chemical compound COC1=CC=C(C)C=C1CCN SMZOUWXMTYCWNB-UHFFFAOYSA-N 0.000 description 1
- JAHNSTQSQJOJLO-UHFFFAOYSA-N 2-(3-fluorophenyl)-1h-imidazole Chemical compound FC1=CC=CC(C=2NC=CN=2)=C1 JAHNSTQSQJOJLO-UHFFFAOYSA-N 0.000 description 1
- OEPOKWHJYJXUGD-UHFFFAOYSA-N 2-(3-phenylmethoxyphenyl)-1,3-thiazole-4-carbaldehyde Chemical compound O=CC1=CSC(C=2C=C(OCC=3C=CC=CC=3)C=CC=2)=N1 OEPOKWHJYJXUGD-UHFFFAOYSA-N 0.000 description 1
- NIXOWILDQLNWCW-UHFFFAOYSA-N 2-Propenoic acid Natural products OC(=O)C=C NIXOWILDQLNWCW-UHFFFAOYSA-N 0.000 description 1
- NLHHRLWOUZZQLW-UHFFFAOYSA-N Acrylonitrile Chemical compound C=CC#N NLHHRLWOUZZQLW-UHFFFAOYSA-N 0.000 description 1
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- 229920000742 Cotton Polymers 0.000 description 1
- 239000004278 EU approved seasoning Substances 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- 102000004190 Enzymes Human genes 0.000 description 1
- 108090000790 Enzymes Proteins 0.000 description 1
- VGGSQFUCUMXWEO-UHFFFAOYSA-N Ethene Chemical compound C=C VGGSQFUCUMXWEO-UHFFFAOYSA-N 0.000 description 1
- JIGUQPWFLRLWPJ-UHFFFAOYSA-N Ethyl acrylate Chemical compound CCOC(=O)C=C JIGUQPWFLRLWPJ-UHFFFAOYSA-N 0.000 description 1
- 239000005977 Ethylene Substances 0.000 description 1
- 229910001335 Galvanized steel Inorganic materials 0.000 description 1
- 240000001585 Limonium sinuatum Species 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- VVQNEPGJFQJSBK-UHFFFAOYSA-N Methyl methacrylate Chemical compound COC(=O)C(C)=C VVQNEPGJFQJSBK-UHFFFAOYSA-N 0.000 description 1
- GYCMBHHDWRMZGG-UHFFFAOYSA-N Methylacrylonitrile Chemical compound CC(=C)C#N GYCMBHHDWRMZGG-UHFFFAOYSA-N 0.000 description 1
- ISWSIDIOOBJBQZ-UHFFFAOYSA-N Phenol Chemical compound OC1=CC=CC=C1 ISWSIDIOOBJBQZ-UHFFFAOYSA-N 0.000 description 1
- 239000004695 Polyether sulfone Substances 0.000 description 1
- 239000004698 Polyethylene Substances 0.000 description 1
- 229920002367 Polyisobutene Polymers 0.000 description 1
- 239000004721 Polyphenylene oxide Substances 0.000 description 1
- 229920002396 Polyurea Polymers 0.000 description 1
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 description 1
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 1
- 229920002472 Starch Polymers 0.000 description 1
- 229910052770 Uranium Inorganic materials 0.000 description 1
- BZHJMEDXRYGGRV-UHFFFAOYSA-N Vinyl chloride Chemical compound ClC=C BZHJMEDXRYGGRV-UHFFFAOYSA-N 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 239000008186 active pharmaceutical agent Substances 0.000 description 1
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- 229930013930 alkaloid Natural products 0.000 description 1
- XYLMUPLGERFSHI-UHFFFAOYSA-N alpha-Methylstyrene Chemical compound CC(=C)C1=CC=CC=C1 XYLMUPLGERFSHI-UHFFFAOYSA-N 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 230000000844 anti-bacterial effect Effects 0.000 description 1
- 238000009360 aquaculture Methods 0.000 description 1
- 244000144974 aquaculture Species 0.000 description 1
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- 229920003235 aromatic polyamide Polymers 0.000 description 1
- 239000010425 asbestos Substances 0.000 description 1
- 235000013361 beverage Nutrition 0.000 description 1
- CQEYYJKEWSMYFG-UHFFFAOYSA-N butyl acrylate Chemical compound CCCCOC(=O)C=C CQEYYJKEWSMYFG-UHFFFAOYSA-N 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 229910000019 calcium carbonate Inorganic materials 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
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- 239000000969 carrier Substances 0.000 description 1
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- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
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- 229910052749 magnesium Inorganic materials 0.000 description 1
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- ZLNQQNXFFQJAID-UHFFFAOYSA-L magnesium carbonate Chemical compound [Mg+2].[O-]C([O-])=O ZLNQQNXFFQJAID-UHFFFAOYSA-L 0.000 description 1
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- 229910000021 magnesium carbonate Inorganic materials 0.000 description 1
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- 239000000395 magnesium oxide Substances 0.000 description 1
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 1
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 description 1
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- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
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- LVHBHZANLOWSRM-UHFFFAOYSA-N methylenebutanedioic acid Natural products OC(=O)CC(=C)C(O)=O LVHBHZANLOWSRM-UHFFFAOYSA-N 0.000 description 1
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Landscapes
- Water Treatment By Sorption (AREA)
Description
【発明の詳細な説明】
本発明は廃水処理、水の再利用処理における固形物除去
、油分除去、エマルジョン除去等の機能を有する水の処
理法に係る。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a water treatment method having functions such as solid matter removal, oil removal, and emulsion removal in wastewater treatment and water reuse treatment.
最近の石油化学、高分子化学、合成繊維、医薬品、鉄鋼
、機械、運搬機具等の工業の飛躍的な発展、人口の大都
市への集中、生活水準の向上によって、環境汚染問題、
生産ラインの水、空気、ガス等のクローズドシステム化
問題などが社会問題として大きくクローズアップされて
来て居り、これに対応して各種の大気及び水質に関する
法規制の強化、製品の安全基準の強化が益々強力に推し
進められつつあることは、衆知の事実である。The recent rapid development of industries such as petrochemicals, polymer chemicals, synthetic fibers, pharmaceuticals, steel, machinery, and transportation equipment, the concentration of the population in large cities, and the improvement of living standards have led to environmental pollution problems.
The problem of closed systems for water, air, gas, etc. in production lines has been attracting attention as a social problem, and in response, various laws and regulations regarding air and water quality have been strengthened, and product safety standards have been strengthened. It is a well-known fact that this is being promoted more and more strongly.
しかし乍ら、現行の工業技術では一般に技術レベルが高
くなるにつれて、装置価格、建設費、ランニングコスト
が上昇し、操作技術も難しく人件費も高くなるのが実情
である。However, with current industrial technology, the reality is that as the technology level increases, equipment prices, construction costs, and running costs generally rise, and operating techniques become difficult and labor costs also rise.
特に固形物、油分、エマルジョン油分、CODを混合し
ている水の処理においては、処理が困難なために、処理
コストが膨大になり勝ちであった。Particularly in the treatment of water containing solids, oil, emulsion oil, and COD, treatment costs tend to be enormous because treatment is difficult.
本発明者らはかかる現情に鑑み、効果的に処理装置の機
能を利用し、経済的に価値の高い処理技術lこ関し、鋭
意研究を進めた結果、本発明を完成した。In view of the current situation, the present inventors have completed the present invention as a result of intensive research into economically valuable processing technology that effectively utilizes the functions of processing devices.
すなわち本発明の要旨とするところは、砂濾過工程と吸
着工程とから成る処理工程により、水を処理するに際し
、水を予め砂濾過工程で処理し、次いで吸着工程で処理
すること、及び吸着工程で用いる吸着材が処理対象物に
対して物理化学的に活性能を有する物質と一体化状態に
ある担体とから構成されていることを特徴としている水
の処理法に係る。That is, the gist of the present invention is that when water is treated by a treatment process consisting of a sand filtration process and an adsorption process, the water is first treated in the sand filtration process, then treated in the adsorption process, and the adsorption process The present invention relates to a water treatment method characterized in that the adsorbent used in the method is composed of a substance that is physicochemically active toward the object to be treated and a carrier in an integrated state.
砂濾過工程は緩速濾過、急速濾過、助剤沢過いずれでも
良く、槽、塔、もしくはカートリッジ容器が用いられる
。The sand filtration process may be slow filtration, rapid filtration, or auxiliary filtration, and a tank, tower, or cartridge container is used.
炉材は本発明に関する限り、一般の砂の他にアンスラサ
イトやザクロ石、樹脂粒、造粒砂、イオン交換樹脂等を
用いることができる。As far as the present invention is concerned, as the furnace material, in addition to general sand, anthracite, garnet, resin particles, granulated sand, ion exchange resin, etc. can be used.
沢材の支持体として砂利等を用いてもよい。Gravel or the like may be used as a support for the swamp material.
流水は上向流、下向流、上下向流等に限定されないし、
水平流濾過、移動床渥過でもよい。Flowing water is not limited to upward flow, downward flow, up-down flow, etc.
Horizontal flow filtration or moving bed filtration may also be used.
砂p過塔は、必要に応じて下部集水装置、逆洗用の各装
置、表面洗浄装置、各種弁、管類を取付けることが出来
る。The sand filter tower can be equipped with a lower water collection device, backwashing devices, surface cleaning devices, various valves, and pipes as necessary.
また流量調節装置、空気抜き、のぞき窓、サイドマンホ
ール等も設けても良い。Additionally, a flow rate adjustment device, air vent, peephole, side manhole, etc. may also be provided.
また必要に応じマイクロフロック沢過、薬注濾過及び接
触渥退的使用も差支えない。Further, microfloc filtration, chemical injection filtration, and contact repulsion may be used as necessary.
砂濾過の槽もしくは塔は、1基に限定されるものではな
く、必要に応じ設置できる。The number of sand filtration tanks or towers is not limited to one, and can be installed as needed.
砂濾過の前段処理には、凝集沈澱処理、加圧浮上処理、
API処理、PPI処理、CPI処理、電解浮上処理等
自由に撰択できるし、既設の処理設備の高次処理として
本発明の処理方法を追加することも出来る。Pre-processing of sand filtration includes coagulation sedimentation treatment, pressure flotation treatment,
API treatment, PPI treatment, CPI treatment, electrolytic levitation treatment, etc. can be freely selected, and the treatment method of the present invention can be added as a higher-level treatment to existing treatment equipment.
砂濾過工程の処理条件としての沢過速度は、処理対象物
の性状によって変えれば良く、一般には0、1 m/4
(〜60 m/Hであるが、これに限定はされない。The flow rate as a processing condition in the sand filtration process may be changed depending on the properties of the object to be processed, and is generally 0 or 1 m/4.
(~60 m/H, but not limited to this.
吸着工程は吸着槽、塔、もしくはカートリッヂ容器が用
いられる。In the adsorption process, an adsorption tank, tower, or cartridge container is used.
吸着槽、塔等は、一系列に限定されるものではなく、二
系列以上を同時に、或は交互に用いても良い。The adsorption tank, tower, etc. are not limited to one series, and two or more series may be used simultaneously or alternately.
逆洗や表面洗浄を実施できるようにしても良い。It may be possible to perform backwashing or surface cleaning.
砂濾過から漏れて流入する固形物を除去するためのフィ
ルター等を吸着工程に取り入れても良い。A filter or the like for removing solid matter leaking from the sand filtration and flowing in may be incorporated into the adsorption process.
浮上性の油分、サスペンション油などの含有量の多い場
合は吸着材を砂濾過と本吸着工程との間に設けることも
出来る。If the content of floating oil, suspension oil, etc. is large, an adsorbent may be provided between the sand filtration and the main adsorption step.
吸着工程で用いる容器中に充填する材料は単独でも、2
種以上の混合物であっても勿論構わない。The material to be filled into the container used in the adsorption process may be 2
Of course, it may be a mixture of more than one species.
充填材料の形状は粉末状、粒状、果粒状、フレーク状、
繊維状、紐状、綿状、フィブリル状、パルプ繊維状、小
塊状、コイル状、ネット状、布帛状などが例示されるが
、特にこれらに限定されない。The shape of the filling material is powder, granule, fruit, flake,
Examples include fibrous, string, cotton, fibril, pulp fiber, small block, coil, net, and fabric, but are not particularly limited thereto.
充填物としては、処理対象物に対して物理化学的に活性
能を有する物質と一体化状態にある担体とから構成され
た物が用いられる。As the filling material, a material composed of a substance that is physicochemically active against the object to be treated and a carrier in an integrated state is used.
物理化学的に活性能を有する物質としては、(1)各種
の活性炭、骨炭、石炭、コークス、副次的に産出される
すす、モレキュラーシーピンクカーボンなどの炭素質材
、(2)シリカゲル、アルミナゲル、活性アルミナ、活
性白土、ゼオライト系モレキュラーシーブス等のシリカ
アルミナ系材、(3)構成成分の少なくとも一種として
Mg、Pb、Fe、Co。Substances that have physicochemically active ability include (1) carbonaceous materials such as various activated carbons, bone charcoal, coal, coke, soot produced by-products, and molecular sea pink carbon, (2) silica gel, alumina silica-alumina-based materials such as gel, activated alumina, activated clay, and zeolite-based molecular sieves; (3) Mg, Pb, Fe, and Co as at least one of the constituent components;
Ni、Cuの群から選ばれた金属の酸化物、水酸化物、
又はその塩を含む無機微粒子が挙げられる。oxides and hydroxides of metals selected from the group of Ni and Cu;
or inorganic fine particles containing a salt thereof.
又、担体としてはスチレン、α−メチルスチレン、ジク
ロルスチレン、その他のスチレン誘導体、メタクリル酸
メチル、アクリル酸エチル、アクリル酸ブチル等のアク
リル酸、又はメタクリル酸のエステル誘導体、エチレン
プロピレン、酢酸ビニル、塩化ビニル、塩化ビニリデン
、アクリロニトリル、メタクリロニトリル等のエチレン
系不飽和単量体、又はブタジェン、イソプレンなどのジ
エン系単量体からなる単独重合体又は共重合体、上記重
合体とアクリル酸、メタクリル酸、イタコン酸等の不飽
和カルボン酸との共重合体、その他としてポリウレタン
、ポリ尿素、ポリエチレンテレフタレート、ポリイソブ
チレンテレフタレート、芳香族ポリアミド、ポリスルフ
ォン、ポリエーテルスルフォン、ポリフェニレンオキサ
イド、ポリカーボネイト等が挙げられる。In addition, as carriers, styrene, α-methylstyrene, dichlorostyrene, other styrene derivatives, ester derivatives of acrylic acid or methacrylic acid such as methyl methacrylate, ethyl acrylate, and butyl acrylate, ethylene propylene, vinyl acetate, Homopolymers or copolymers consisting of ethylenically unsaturated monomers such as vinyl chloride, vinylidene chloride, acrylonitrile, and methacrylonitrile, or diene monomers such as butadiene and isoprene, and the above polymers and acrylic acid and methacrylic acid. Acids, copolymers with unsaturated carboxylic acids such as itaconic acid, and others include polyurethane, polyurea, polyethylene terephthalate, polyisobutylene terephthalate, aromatic polyamide, polysulfone, polyethersulfone, polyphenylene oxide, polycarbonate, and the like.
カートリッヂを用いる場合には、吸着材を内蔵する胴缶
及び開缶可能なふたとから構成され使用時に必要に応じ
、開缶が可能な交換及び保存の容易なものを用いるのが
好ましい。When using a cartridge, it is preferable to use a cartridge that is easy to replace and store, and is composed of a body can containing an adsorbent and a lid that can be opened, and can be opened as needed during use.
本発明で言う胴缶とは、形状としてはその断面が円、だ
円、三角、四角、多角形等であり、材質としては、金属
、木、紙、ガラス、合成樹脂、とう器等であり、使用前
の状態では胴缶とふたで構成された内部に充填剤を密閉
状態で内蔵している。In the present invention, the body can has a cross section of a circle, an ellipse, a triangle, a square, a polygon, etc., and is made of metal, wood, paper, glass, synthetic resin, a container, etc. Before use, the filler is sealed inside the can and the lid.
胴缶は、カートリッジエレメントの使用時の内圧、カー
トリッジを使用するためのハウジングにセットするため
の外圧、カートリッジ間、カートリッジとハウジング間
のシールのための圧力、及びハウジングからカートリッ
ジを撤去する際の外力に対して必要な強度を有している
。The body can handle internal pressure when using the cartridge element, external pressure for setting the cartridge in the housing for use, pressure for sealing between the cartridges and between the cartridge and the housing, and external force when removing the cartridge from the housing. It has the necessary strength.
具体的には、金属の場合10μ以上の厚み、紙製の場合
は防水及び撥水処理を施こし、使用時の吸湿による強度
低下を防ぐ必要があり、200μ以上の厚み、ガラスの
場合は1nm以上の厚み、合成樹脂の場合は50μ以上
の厚みが好ましい。Specifically, if it is made of metal, it must be at least 10μ thick; if it is made of paper, it must be treated with waterproof and water-repellent treatment to prevent strength loss due to moisture absorption during use, and if it is made of paper, it must be at least 200μ thick; if it is made of glass, it must be 1nm. In the case of synthetic resin, the thickness is preferably 50μ or more.
胴缶は2種以上の材料の複合材でも良し、ラミネートシ
ートなどから出来ていても良い。The body can may be made of a composite material of two or more materials, or may be made of a laminate sheet or the like.
胴缶は無数の孔のある材料であっても良く、この場合は
、保存中は更に外周にシールするためのシート、フィル
ム、テープ、金属箔などを貼りつけることによって充填
材の保護が行なえる。The can body may be made of a material with numerous holes, and in this case, the filling material can be further protected during storage by attaching a sealing sheet, film, tape, metal foil, etc. to the outer periphery. .
胴缶内には、充填物の性質及び用途によっては、スクリ
ーンや二重、三重の筒を保持するための凸起やアタッチ
メント、シールのためのアタッチメント、目皿を置くた
めのスペースや、胴缶の外側には開缶可能なふたをとり
つけるためのアタッチメント、凸部、凸部、段、ネジ山
、シールテープのための面等が存在する。Depending on the nature and purpose of the filling, there may be protrusions or attachments for holding screens, double or triple cylinders, attachments for sealing, space for perforated plates, and space inside the can body, depending on the nature and purpose of the filling. On the outside of the can, there are attachments for attaching an openable lid, protrusions, protrusions, steps, threads, a surface for sealing tape, etc.
シールのために充填材を接着剤や膨潤剤によって充填剤
と壁を一体化させることも出来る。It is also possible to integrate the filler with the wall using adhesives or swelling agents for sealing purposes.
胴缶のふたは胴缶と一体化したものでも独立したもので
も良いが、必要時に直ちに開缶できる必要から、取はず
しが容易、もしくは簡単な器具で開缶できるようになっ
ている必要がある。The lid of the can body can be integrated with the can body or can be independent, but since it is necessary to be able to open the can immediately when necessary, it must be easy to remove or can be opened using a simple device. .
缶が密閉出来るために長距離の運搬、長時間の保存液状
物を含んでいる際にも利用出来る。Since the can can be sealed tightly, it can be used for long-distance transportation and when containing liquid substances that can be stored for a long time.
又、塔の中に編織物、網などの袋の中に入れた吸着材を
充填しても良い。Alternatively, the tower may be filled with an adsorbent placed in a bag made of knitted fabric, net, or the like.
塔を2重構造とし、内部の塔、または容器に吸着材を入
れ、取り出し時は、この内部の塔または容器と一緒に取
り出しても良い。The tower may have a double structure, and the adsorbent may be placed in the internal tower or container, and the adsorbent may be taken out together with the internal tower or container.
本発明の処理対象を例示すると次の通りである。Examples of objects to be processed by the present invention are as follows.
(1)各種の産業廃水、すなわち鉄鋼圧延工場、ステン
レス圧延工場、アルミ圧延工場、石油精製工場、機械工
場、塗装工場、メッキ工場、レンズ等の研磨工場、医薬
品製造工場、飲食品製造並びに加工工場、動構油加工場
、各種機器洗工場、脱脂洗滌工場、精練染色工場、金属
加工及び伸縮工場、水産化工工場等の廃水
(2)各種洗車整備場の廃水、すなわち、バス、ブルド
ーザ−1車輛、航空機、自家用車、電車、競技用自動車
、競技用ボート、競技用自動車の洗車、修理、組立、整
備工場、ガソリンスタンド、タンク洗浄水等
(3)各種の船舶からの廃水、すなわちタンククリーニ
ング水、ビルジ水、バラスト水、ドック排水、船舶建造
及び整備場からの廃水、甲板からの流出水等
(4)各種循環水すなわち、ボイラー水、ホテル内循環
水、プールや養殖池の循環水、工場内洗浄水、発電所冷
却水、油槽所廃水等
(5)下水処理場、ちゅう房排水等
(6)海、湖、沼及び河川等の流出した廃水の処理(7
)用水の清澄化
(8)研究所、試験所、検査場、病院等
(9)各種工場(こおける製造プロセスへの適用すなわ
ち製糖工業、でんぷん工業、乳製品工業、醸造工業、食
用油工業、工業用油剤及び油剤工業、ゴム工業、石油精
製及び化学工業、高分子化学工業、染料染色工業、無機
薬品工業、金属工業、ドライクリーニング液等における
液相での精製
(10)各種工業における捕集または回収、すなわち医
薬品工業における抗菌性物質、ビタミン、ホルモン、酵
素、核酸系その他の生化学薬品、アルカロイド等、食品
工業における核酸系調味料、植物成分等、ガス工業にお
けるフェノール等、沃素工業における沃素等、鉱業にお
ける金、銀、パラジウム、オスミウム、水銀、ウラン、
鉛、亜鉛、銅等、その池水中の有機溶剤成分等の吸着
aυ 各種分析、テストへの応用
(L2)上水道における原水の汚濁物質、異臭味、洗剤
、農薬などの除去
03)処理水の再利用システムへの応用
以上であるが、本発明はこれに限定されない。(1) Various types of industrial wastewater, including steel rolling mills, stainless steel rolling mills, aluminum rolling mills, oil refineries, machine factories, painting factories, plating factories, lens polishing factories, pharmaceutical manufacturing factories, food and beverage manufacturing and processing factories (2) Wastewater from various car wash and maintenance facilities, including buses, bulldozers, etc. , aircraft, private cars, trains, competition cars, competition boats, competition car washing, repair, assembly, maintenance shops, gas stations, tank cleaning water, etc. (3) Wastewater from various ships, i.e. tank cleaning water , bilge water, ballast water, dock drainage, wastewater from ship construction and maintenance yards, runoff from decks, etc. (4) Various types of circulating water, including boiler water, circulating water in hotels, circulating water from pools and aquaculture ponds, and factories. Internal cleaning water, power plant cooling water, oil depot wastewater, etc. (5) Sewage treatment plants, cell drainage, etc. (6) Treatment of wastewater from the sea, lakes, marshes, rivers, etc. (7)
) Clarification of water (8) Research laboratories, testing stations, inspection stations, hospitals, etc. (9) Various factories (application to manufacturing processes in the sugar industry, starch industry, dairy industry, brewing industry, edible oil industry, etc.) Purification in liquid phase in industrial oil and oil industry, rubber industry, petroleum refining and chemical industry, polymer chemical industry, dyeing industry, inorganic chemical industry, metal industry, dry cleaning liquid, etc. (10) Collection in various industries or recovery, i.e. antibacterial substances, vitamins, hormones, enzymes, nucleic acid-based and other biochemicals, alkaloids, etc. in the pharmaceutical industry, nucleic acid-based seasonings, plant ingredients, etc. in the food industry, phenol, etc. in the gas industry, iodine in the iodine industry. etc., gold, silver, palladium, osmium, mercury, uranium in mining, etc.
Adsorption aυ of organic solvent components in pond water such as lead, zinc, copper, etc. Application to various analyzes and tests (L2) Removal of pollutants, off-flavors, detergents, agricultural chemicals, etc. from raw water in water supplies 03) Recycling of treated water Although the present invention is not limited to this application, the present invention is not limited thereto.
吸着工程の後工程さして、必要に応じ活性炭処理、イオ
ン交換樹脂処理、電気透析法による処理、逆浸透圧法に
よる処理等を組合せることができる。As a post-adsorption step, activated carbon treatment, ion exchange resin treatment, electrodialysis treatment, reverse osmosis treatment, etc. can be combined as necessary.
またPH調整槽等の工程を追加させることも可能である
。It is also possible to add steps such as a PH adjustment tank.
以下、本発明の例を図に従って詳述する。Examples of the present invention will be described in detail below with reference to the drawings.
第1図は、本発明の処理方法のフローシートの例の説明
図である。FIG. 1 is an explanatory diagram of an example of a flow sheet of the treatment method of the present invention.
図中1は原廃水槽、2はストレーナ−13はポンプ、4
は砂沢過塔、5は吸着塔、6はサイフオンブレーカ−1
7は処理水槽、8は逆洗水用ポンプであり、廃水はスト
レーナ−2を介してポンプ3によって砂涙過塔4へ圧送
すれ、固形物を除去した後、吸着塔5へ圧送され、油分
、エマルジョンオイル、CODを除去した後、サイフオ
ンブレーカ−6によって大気圧に一旦戻された後処理水
槽7に排出される。In the figure, 1 is the original wastewater tank, 2 is the strainer, 13 is the pump, and 4
is Sunazawa filter tower, 5 is adsorption tower, 6 is siphon breaker-1
7 is a treated water tank, and 8 is a pump for backwash water. Waste water is pumped through a strainer 2 by a pump 3 to a sand filter tower 4 to remove solids, and then pumped to an adsorption tower 5 to remove oil. , emulsion oil, and COD are removed, the water is once returned to atmospheric pressure by a siphon breaker 6 and discharged into a post-treatment water tank 7 .
砂p過塔が固形物を涙過した結果目詰りを生じ圧力が高
くなった場合は逆洗水用ポンプ3によって処理水槽7よ
り砂涙過塔4に処理時の流れ方向とは反対方向に処理水
を流し固形物を洗い落とす。If the sand filtering tower becomes clogged and the pressure increases as a result of passing solids, the backwash water pump 3 transfers the water from the treatment water tank 7 to the sand filtering tower 4 in the opposite direction to the flow direction during treatment. Rinse away the solids by flushing the treated water.
第2図はカートリッジエレメントを用いるS合の例を示
す説明図である。FIG. 2 is an explanatory diagram showing an example of S combination using a cartridge element.
第2図は、処理対象の特性上、充填材との接触時間を長
くとる必要のある場合、−または数種類の充填材を順次
通過させる必要のある場合の例であって、アタッチメン
ト9゜14、カートリッジエレメント10,11,12
゜13、パイプ15.16から構成され、処理対象物は
パイプ16から送りこまれ、アタッチメント14からカ
ートリッジエレメント13から順次10にまで上に向っ
て流れて処理され、アタッチメント9によって処理後の
ものが集められ、パイプ15から排出される方式である
。FIG. 2 shows an example of a case where it is necessary to take a long time in contact with the filler due to the characteristics of the object to be treated, or when it is necessary to pass several types of filler in sequence. Cartridge elements 10, 11, 12
13, and pipes 15 and 16, the object to be treated is sent from the pipe 16, flows upward from the attachment 14 to the cartridge element 13 and then sequentially to 10 for treatment, and the attachment 9 collects the treated object. This is a system in which the water is collected and discharged from a pipe 15.
第3図は、密閉容器18の中にカートリッジエレメント
17をセットした例を示しており、カートリッジエレメ
ント17の上ぶたは開放されたままであり、下ぶたは取
はずしたあと、密閉容器18の中に設置したカートリッ
ジエレメント17とのジヨイント20の上部にはめこま
れており、処理対象物は、パイプ21から密閉容器の上
部19へ送りこまれ、カートリッジエレメント17で処
理されてパイプ22から外部に排出されるものであり、
小規模の処理装置として効果的で取扱いも容易であると
いう特徴を有している。FIG. 3 shows an example in which the cartridge element 17 is set in the airtight container 18.The upper lid of the cartridge element 17 remains open, and after removing the lower lid, the cartridge element 17 is placed inside the airtight container 18. It is fitted into the upper part of the joint 20 with the installed cartridge element 17, and the object to be treated is sent from the pipe 21 to the upper part 19 of the closed container, processed by the cartridge element 17, and discharged to the outside from the pipe 22. It is a thing,
It has the characteristics of being effective as a small-scale processing device and easy to handle.
実施例 1
コンプレッサーから排出されるエアーコンプレッサード
レンを処理する方法として、次の処理プロセスを組んだ
。Example 1 The following treatment process was set up as a method for treating air compressor drain discharged from a compressor.
すなわち、ニアコンプレッサードレン(以下廃水と略記
する)に含まれる浮遊固形分(以下SSと略記する)を
除去する砂濾過工程と廃水中に含まれる油分、エマルジ
ョンオイルを吸着除去する吸着除去工程とからなり、こ
の両生工程の作用効果及び作業性を高めるための関連設
備とから構成させた。That is, a sand filtration step removes suspended solids (hereinafter referred to as SS) contained in the near compressor drain (hereinafter referred to as wastewater), and an adsorption removal step removes oil and emulsion oil contained in the wastewater. The system was designed to include related equipment to improve the effectiveness and workability of this amphibious process.
処理システムのフローシートは、第1図の通りであり、
各ユニットの名称は本文説明の通りである。The flow sheet of the treatment system is shown in Figure 1.
The name of each unit is as explained in the text.
廃水中のSSを除去するユニットプロセスは以下説明の
仕様の砂濾過塔を用いた。The unit process for removing SS from wastewater used a sand filtration tower with the specifications described below.
直径が1130mm、高さが1900mmの一般構造用
圧延鋼材JISG3101の5S50で製作した円筒型
の筒を塔とし、底部Eこは厚み10mrnの鋼板に5m
rnφの孔を加工したものを用いた。The tower is a cylindrical tube made of general structural rolled steel material JIS G3101 5S50 with a diameter of 1130 mm and a height of 1900 mm.
A material with holes of rnφ was used.
底部には外部に通じる75mmφの孔を設け、パイプに
連結した。A 75 mmφ hole communicating with the outside was provided at the bottom and connected to a pipe.
パイプは水道用亜鉛メッキ鋼管JISG3442の5G
PWである。The pipe is a galvanized steel pipe JIS G3442 5G for water service.
It is PW.
塔内の涙材は下記のように砂利、砂及びアンスラサイト
を用いた。Gravel, sand, and anthracite were used for the lacrimal materials in the tower as shown below.
塔の上部から廃水を送りこみ底部から処理水を排出する
いわゆる下向流方式で廃水を処理する方式とした。The wastewater was treated using the so-called downward flow method, in which wastewater is sent from the top of the tower and treated water is discharged from the bottom.
砂及びアンスラサイトにSSが捕捉された結果目詰りが
起り、差圧(以下△Pと略記する)が高くなった場合は
処理を中止し、塔の底部から上部に向って、すなわち上
向流水を流し、砂及びアンスラサイト中に捕捉されてい
るSSを洗い落とすための逆洗システムを設けた。If clogging occurs as a result of SS being trapped in the sand and anthracite, and the differential pressure (hereinafter abbreviated as △P) increases, the treatment is stopped and the water flows upward from the bottom to the top of the tower. A backwash system was installed to wash away the SS trapped in the sand and anthracite.
処理時にはポンプによって下向流で水が流れ、逆洗時に
は逆洗ポンプによって上向流で水が流れるようにした。During treatment, a pump caused water to flow downward, and during backwashing, a backwash pump caused water to flow upward.
塔の上部には塔内空気抜き用のコックを取りつけた。A cock was installed at the top of the tower to vent air from inside the tower.
塔内の圧力を検出するための圧力計を塔に取りつけた。A pressure gauge was attached to the tower to detect the pressure inside the tower.
圧力計は最大検出能力5kg/ff1Gのものである。The pressure gauge has a maximum detection capacity of 5 kg/ff1G.
塔の下部側面には、塔内洗浄、補修及び砂やアンスラサ
イトの交換のためのサイドマンホールを設けた。A side manhole was installed on the lower side of the tower for cleaning, repairing, and replacing sand and anthracite inside the tower.
サイドマンホールの径は480mmである。SSを除去
した処理水は次いで、マグネシウム系無機質を含むエマ
ルジョンオイル吸着材によってエマルジョン化している
コンプレッサードレンを吸着除去するユニットプロセス
に依り処理した。The diameter of the side manhole is 480 mm. The treated water from which SS had been removed was then treated in a unit process in which emulsified compressor drain was adsorbed and removed by an emulsion oil adsorbent containing a magnesium-based inorganic substance.
直径が1130朋、高さが1050mmの塔の中に下記
の条件でエマルジョンオイル吸着材を充填した。An emulsion oil adsorbent was packed into a tower having a diameter of 1130 mm and a height of 1050 mm under the following conditions.
尚、塔の材料、及び配管材料は砂p過塔と同じものを用
いた。The materials for the tower and piping were the same as those for the sand filter tower.
ここでエマルジョンオイル吸着材は次の方法で製造した
ものを用いた。The emulsion oil adsorbent used here was manufactured by the following method.
ヨード数301nI?/gの酸化マグネシウム粉末80
部、メルトインデックスが0.3の高密度ポリエチレン
20部、及び塩化メチレン400部からなる混合物をオ
ートクレープ中に仕込み、密閉して窒素ガスにより初期
圧力として10 kg/cfflGをかけ、毎分400
回転の速度で撹拌しつつジャケットによりオートクレー
ブの内温を180℃にまで上昇せしめたところ、内部の
圧力が38kg/cvtGまで上昇した。Iodine number 301nI? /g magnesium oxide powder 80
1, 20 parts of high-density polyethylene with a melt index of 0.3, and 400 parts of methylene chloride were charged into an autoclave, the autoclave was sealed, and an initial pressure of 10 kg/cfflG was applied with nitrogen gas, and the autoclave was heated at 400 parts per minute.
When the internal temperature of the autoclave was raised to 180° C. using a jacket while stirring at a rotating speed, the internal pressure rose to 38 kg/cvtG.
さらに窒素ガスtこより内部の圧力を50 kg、/c
r?LGまで上昇せしめた状態で撹拌しつつ5分間保持
した後、オートクレーブの底部にある直径1.0mmの
オリフィスより内部の懸濁液を噴出させ、同時に押出さ
れた長さ15mm、直径約5μのフィブリル状物を構成
単位とする微細複合体をオリフィス直下50071!7
1!のところで捕集し、その後シングルディスク型リフ
ァイナーにより、濃度1.0%、ケージクリアランス3
mmの条件でリファイニング処理を施こし、次いで毎分
150回転の速度で撹拌しつつ、ガラス繊維(等量)と
混合し、自然脱水によってエマルジョンオイル吸着材を
得た。Furthermore, the internal pressure was increased to 50 kg/c using nitrogen gas.
r? After raising the temperature to LG and holding it for 5 minutes while stirring, the internal suspension was jetted out from an orifice with a diameter of 1.0 mm at the bottom of the autoclave, and at the same time a fibril with a length of 15 mm and a diameter of about 5 μ was extruded. 50071!7 A microscopic composite whose constituent units are 50071!7 directly below the orifice.
1! After that, it was collected at
A refining treatment was performed under the conditions of 1.5 mm, followed by mixing with glass fiber (equal amount) while stirring at a speed of 150 revolutions per minute, and natural dehydration to obtain an emulsion oil adsorbent.
リファイニング処理、及びガラス繊維との混合時の媒体
としては通常の水道水を用いた。Ordinary tap water was used as a medium during the refining process and during mixing with glass fibers.
吸着塔の内部の水位はエマルジョンオイル吸着材の表面
以上になるようにサイフオンブレーカ−のブレーク点の
高さを吸着材の高さより250mm高くした。The height of the break point of the siphon breaker was set 250 mm higher than the height of the adsorbent so that the water level inside the adsorption tower was higher than the surface of the emulsion oil adsorbent.
逆洗用の水源は本処理システムによる処理水を用い、逆
洗によって生じた逆洗水は廃水の原水槽に戻した。Water treated by this treatment system was used as the water source for backwashing, and the backwash water generated by backwashing was returned to the wastewater raw water tank.
吸着材の使用済みのものは、サイドマンホールより取り
出し、一昼夜自然脱水した後、プラスチックの専用焼却
炉で焼却した。The used adsorbents were taken out from the side manhole, naturally dehydrated for a day and night, and then incinerated in a special plastic incinerator.
処理条件は次の通りとした。The processing conditions were as follows.
以上の条件での処理の結果、次の処理水が得られた。As a result of the treatment under the above conditions, the following treated water was obtained.
運転時間34時間で△Pが逆洗指示圧2.5 kg/=
Gに達したので、30分間逆洗した。In 34 hours of operation time, △P is backwashing pressure 2.5 kg/=
Since it reached G, I backwashed it for 30 minutes.
条件は次の通りであった。The conditions were as follows.
本実施例で得た処理水の水質は再使用に充分なレベルに
あったので設備洗滌用水として再利用したが全く問題が
なかった。The quality of the treated water obtained in this example was at a level sufficient for reuse, so it was reused as equipment washing water without any problems.
比較例
実施例1の吸着塔の中に市販の吸油材であるポリプロピ
レン繊維を80kg充填した。Comparative Example The adsorption tower of Example 1 was filled with 80 kg of polypropylene fiber, which is a commercially available oil-absorbing material.
処理条件を実施例1にあわせた時の結果 SS 21ppm ノルマヘキサン抽出物 405ppIn COD 45ppm であった。Results when processing conditions were adjusted to Example 1 SS 21ppm Normal hexane extract 405ppIn COD 45ppm Met.
この廃水は通常の吸油材では全く処理出来ないものであ
った。This wastewater could not be treated at all with ordinary oil-absorbing materials.
実施例 2
外径253mm、高さ100朋の胴缶と、直径2001
mのふたを上下にはめこんだ第2図の形状のメッキ鋼板
製の缶を準備し、上下のふたを取りはずした。Example 2 A body can with an outer diameter of 253 mm and a height of 100 mm, and a diameter of 200 mm.
A can made of plated steel plate having the shape shown in Fig. 2 with two lids fitted on the top and bottom was prepared, and the top and bottom lids were removed.
次いで、直径210關の金網を缶の孔から内部に押し入
れ、内部で再び金網を平にして底部において、下ぶたの
孔全体を覆おうようにした。Next, a wire mesh with a diameter of 210 mm was pushed into the can through the hole, and inside the can, the wire mesh was again flattened and placed at the bottom so that it covered the entire hole in the lower lid.
次に粘着テープによってこの金網を缶の内部に貼りつけ
て固定した。Next, this wire mesh was attached and fixed to the inside of the can using adhesive tape.
このようにして4個の缶を準備した。Four cans were prepared in this way.
−個目の缶の中には、まず坪量200g/m2のガラス
繊維の平組織の織物を一枚敷き、その上に0.1〜2.
0朋の直径の砂を3kg充填し、その上へ同じガラス繊
維を一枚かぶせた。- Inside each can, first lay a sheet of glass fiber flat-textured fabric with a basis weight of 200 g/m2, and then place 0.1~2.
3 kg of sand with a diameter of 0 mm was filled, and a sheet of the same glass fiber was placed on top of it.
二個消の缶の中には、平均繊度が15デニールのポリプ
ロピレン繊維の不織布を450g充填した。A two-pack can was filled with 450 g of a nonwoven fabric made of polypropylene fibers having an average fineness of 15 deniers.
三個目の缶の中には、水酸化マグネシウムと高密度ポリ
エチレンとが一体化した微細繊維複合体と11μのガラ
ス繊維と3デニールのポリプロピレン繊維の1:1:1
の比率の混合物を1.25kg充填した。Inside the third can is a fine fiber composite made of magnesium hydroxide and high-density polyethylene, 11μ glass fiber and 3 denier polypropylene fiber in a ratio of 1:1:1.
1.25 kg of the mixture having the following ratio was filled.
四個目の缶には、粒径が2〜4mmの粒状活性炭を50
09充填した。The fourth can contains 50 granular activated carbon with a particle size of 2 to 4 mm.
09 was filled.
この様にして揃えた四個の缶を縦に積み重ねて、第2図
の如くアタッチメント9,14の間にカートリッジエレ
メントを配置した。The four cans arranged in this manner were stacked vertically, and the cartridge element was placed between the attachments 9 and 14 as shown in FIG.
カートリッジエレメント間、及びカートリッジエレメン
トと上下のアタッチメントとの間のシールはアスベスト
シートを用いて完全にした。The seals between the cartridge elements and between the cartridge elements and the upper and lower attachments were completed using asbestos sheets.
カートリッジエレメントの配置は
10を砂を充填したもの
11をポリプロピレン繊維を充填したもの12を微細複
合体、ガラス繊維及びポリプロピレン繊維の1:1:1
の比率の混合物を充填したもの
13は粒状活性炭を充填したもの
とし、処理対象物は15のパイプからポンプに依って圧
送され、9のアタッチメントからカートリッジエレメン
ト10.lL12.13を通って処理され、アタッチメ
ント14からパイプ16を通って排出されるようにした
。The arrangement of the cartridge elements is 10 filled with sand, 11 filled with polypropylene fibers, and 12 filled with fine composite, glass fiber and polypropylene fiber in a ratio of 1:1:1.
13 is filled with granular activated carbon, and the object to be treated is pumped from a pipe 15 by a pump, and from an attachment 9 to a cartridge element 10. 12.13 and discharged from attachment 14 through pipe 16.
処理対象物は、機械工場の切削加工工場の廃水とコンプ
レッサードレンである。The objects to be treated are wastewater and compressor drains from the cutting shop of the machine shop.
処理条件は次のようにした。The processing conditions were as follows.
処理量 :毎時0.5.lL’ 処理時間:1日当り8時間 1月当り25日(200時間) 処理結果は第4表の通りであった。Processing amount: 0.5 per hour. lL' Processing time: 8 hours per day 25 days (200 hours) per month The treatment results are shown in Table 4.
ここで、油分及びCODはJISの方法に準じて分析し
た結果である。Here, the oil content and COD are the results of analysis according to the JIS method.
処理を続けたところ約200時間でカートリッジエレメ
ント2の粒状活性炭が処理能力を失ったので直ちにポン
プを停止させ、新しいカートリッジエレメントと取替え
た。As the treatment continued, the granular activated carbon in cartridge element 2 lost its treatment capacity after about 200 hours, so the pump was immediately stopped and replaced with a new cartridge element.
カートリッジエレメントの交換作業は15分間で1名の
作業員の作業で充分な程容易であった。The replacement work of the cartridge element was so easy that it took 15 minutes and was done by one worker.
400時間運転後、カートリッジエレメント4の微細複
合体、ポリプロピレン繊維及びガラス繊維の混合物の効
力の失なわれているのがわかったため交換することとし
た。After 400 hours of operation, it was found that the mixture of fine composite material, polypropylene fibers, and glass fibers in cartridge element 4 had lost its effectiveness, so it was decided to replace it.
この時、すでにカートリッジエレメント5の処理能力の
落ちているのが明らかとなった。At this time, it became clear that the processing capacity of the cartridge element 5 had already decreased.
カートリッジエレメントの寿命としては、4は5の2倍
であることが分ったので粒状活性炭のカートリッジエレ
メントを2段積み重ね、合せて五段のカートリッジエレ
メントをセットすることによって取替の期間を揃え、4
00時間、すなわち2ケ月に一回取替えるだけで良くな
った。As for the lifespan of the cartridge element, it was found that 4 is twice as long as 5, so by stacking two tiers of granular activated carbon cartridge elements and setting a total of five tiers of cartridge elements, the replacement period was equalized. 4
00 hours, that is, it only needs to be replaced once every two months.
カートリッジエレメントを用いたプロセスは処理対象に
応じた組合せが可能であり、最適のフローを組むのが極
めて容易であるという特徴を有している。Processes using cartridge elements are characterized in that combinations can be made depending on the processing target, and it is extremely easy to set up an optimal flow.
実施例 3
発電所及び石油基地の廃水処理のために、次の処理装置
を組んだ。Example 3 The following treatment equipment was constructed to treat wastewater from a power plant and an oil base.
(1)砂濾過塔
■内 径2000m7!L
■ 高 さ 1800mm
■ 涙過面積 3.14m2
■ p過速度 16m/H
■炉材
砂利 10〜301n11L 層高 400mmtt
5〜10mm tt 300mm〃3〜5
7ILrfL〃100mm
粗砂 0.8〜1,9朋 tt 300mm砂0,
3〜0.8mm tt 300mm(2)吸着塔
■ 吸着材
成分 水酸化マグネシウム 60%
アルミナ 10%
エチレン醋ピコポリマー 30%
形状 0.5〜18mrILの寸法の軟質粒状体■塔■
内 径2000ii
@ 高 さ 1500mm
0面 積3.14m2X2塔
○線 速8 m/H
■ 充填密度 0.1 g%兼
(3)ポンプ
■流量60m″/H
■ 揚 程 30m水柱
以上のシステムで処理した結果、第5表を得た。(1) Sand filter tower ■Inner diameter 2000m7! L ■Height 1800mm ■Layer overflow area 3.14m2 ■P overspeed 16m/H ■Furnace gravel 10~301n11L Layer height 400mmtt
5~10mm tt 300mm〃3~5
7ILrfL〃100mm Coarse sand 0.8~1.9 tt 300mm sand 0,
3 to 0.8 mm tt 300 mm (2) Adsorption tower ■ Adsorbent components Magnesium hydroxide 60% Alumina 10% Ethylene picopolymer 30% Shape Soft granules with dimensions of 0.5 to 18 mrIL ■ Tower ■
Inner diameter 2000ii @ Height 1500mm 0 area Area 3.14m2 x 2 towers ○ Linear speed 8 m/H ■ Packing density 0.1 g% and (3) pump ■ Flow rate 60 m''/H ■ Lifting head Processing in a system with a water column of 30 m or more As a result, Table 5 was obtained.
尚、ここで発電所廃水はポリ塩化アルミニウムと炭酸ソ
ーダを用いた凝集沈澱処理後の処理水であり、石油基地
廃水は重力分離処理後、平行傾斜板(CPI法)による
処理水である。Note that power plant wastewater here is treated water after coagulation sedimentation treatment using polyaluminum chloride and soda carbonate, and oil base wastewater is treated water after gravity separation treatment using a parallel inclined plate (CPI method).
実施例 4
バスの洗車廃水機より排出される廃水を処理し、その処
理水を再び洗車用水として用いることを目的とした処理
装置を作成し、連続テストを実施した。Example 4 A treatment device was created for the purpose of treating wastewater discharged from a bus car wash wastewater machine and reusing the treated water as car wash water, and a continuous test was conducted.
装置の構成は、次のようにした。The configuration of the device was as follows.
(1) 砂ア過塔
■ 内径 200mm
■ 高さ 600關
■ p材 アンスラサイト
(2)吸着カートリッジ
■ 市販ベール缶(底部1こ5mmφの孔を6個有する
)
■ 吸着材 ■ポリエチレンと含水
ケイ酸の一体化物 60%
@ポリプロピレン繊維 40%
■ 支持体 ポリプロピレン繊維
シート厚み 121ft7IL
(3)吸入ロストレーナ−60メツシユ
(4)ポンプ
■ 流量 2 m”、/H
■ 揚程 17m
(5)システムの構成
■ ストレーナ−1ケ
■ ポンプ 1ケ
■ 砂p過塔 2ケ
■ 吸着カートリッジ 4ケ
■ カートリッジ容器 1ケ
処理結果は、第6表の通りであった。(1) Sand filter tower ■ Inner diameter 200 mm ■ Height 600 mm ■ P material Anthracite (2) Adsorption cartridge ■ Commercially available bale can (with 6 holes of 5 mm diameter in the bottom) ■ Adsorbent ■ Polyethylene and hydrated silicic acid Integrated product 60% @ polypropylene fiber 40% ■ Support polypropylene fiber sheet thickness 121ft7IL (3) Suction loss strainer - 60 mesh (4) Pump ■ Flow rate 2 m”, /H ■ Lifting height 17 m (5) System configuration ■ Strainer -1 pc ■ Pump 1 pc ■ Sand filter tower 2 pcs ■ Adsorption cartridge 4 pcs ■ Cartridge container 1 pc The treatment results were as shown in Table 6.
これから明らかなように、本発明の処理方法によれば日
間変動の極めて激しい廃水であるにも拘らず安定した処
理水が得られるという特徴が認められた。As is clear from the above, the treatment method of the present invention has the characteristic that stable treated water can be obtained even though the wastewater has extremely large fluctuations from day to day.
また、吸着材のカートリッチは寸法がベール缶を利用し
ているために取扱いが容易であり、交換時の重量もせい
ぜい15kyどまりのため、1名の作業員で補修作業を
終了できるという特徴があった。In addition, the adsorbent cartridge is easy to handle because it uses a bale can, and the weight at the time of replacement is no more than 15 kilograms, so the repair work can be completed by one worker. there were.
実施例 5
凝集加圧浮上処理によって生じたスカムを砂濾過池で分
離し、その沢過水を吸着材の入った槽で処理した。Example 5 Scum produced by coagulation and pressure flotation treatment was separated in a sand filter basin, and the filtrate was treated in a tank containing an adsorbent.
凝集加圧浮上処理は、ポリ塩化アルミニウム、苛性ソー
ダ、高分子潔集剤で行なうものであり、そのためスカム
は軟質のスラツヂ状であった。The agglomeration and pressure flotation treatment was carried out using polyaluminum chloride, caustic soda, and a polymer scouring agent, so the scum was in the form of a soft sludge.
砂利300mm、砂400mmの層からなる砂濾過池で
あり表面積を3m2とした。It is a sand filter pond consisting of a layer of 300 mm of gravel and 400 mm of sand, and has a surface area of 3 m2.
水量は1m2/Hであった。The amount of water was 1 m2/H.
吸着工程は次のようにした。直径200mm、高さ20
0mmの上下ぶた付の缶詰用の缶にポリスチレン、炭酸
マグネシウム、水酸化マグネシウムの混合してなる破砕
物を1.2ky充填した。The adsorption process was as follows. Diameter 200mm, height 20
A can with a 0 mm top and bottom lid was filled with 1.2 ky of a crushed mixture of polystyrene, magnesium carbonate, and magnesium hydroxide.
破砕物は、次の様にして作成した。炭酸カルシウム20
部、水酸化マグネシウム20部及びポリスチレン60部
の混合物を205°Cに加熱したロール上で混練した後
冷却し、破砕物で平均粒径2mwに破砕した。The crushed material was created as follows. calcium carbonate 20
A mixture of 20 parts of magnesium hydroxide, and 60 parts of polystyrene was kneaded on a roll heated to 205°C, cooled, and crushed to an average particle size of 2 mw.
缶の底部には、濾紙を金網の上に接着せしめた。At the bottom of the can, filter paper was glued onto a wire mesh.
又、缶の内壁にも、同じ濾紙を接着した。The same filter paper was also glued to the inner wall of the can.
このように内部を濾紙で加工したあと上記の破砕物を充
填した。After the inside was treated with filter paper in this way, the above-mentioned crushed material was filled.
この破砕物を充填した後その上へ繊度が3デニール、長
さ6mmのポリプロピレン繊維を5mm程度の厚みに積
層し、その上へ上記の濾紙をのせて周囲を接着した。After filling this crushed material, polypropylene fibers having a fineness of 3 denier and a length of 6 mm were laminated thereon to a thickness of about 5 mm, and the above-mentioned filter paper was placed on top of it and the surrounding area was adhered.
このようにして得たカートリッジエレメントに対し流速
30m/時の水を15分間流し、養生処理を行なった。The cartridge element thus obtained was subjected to curing treatment by flowing water at a flow rate of 30 m/hour for 15 minutes.
その結果生じた上ぶたとの間の間隙にポリプロピレン繊
維のニードルパンチング法によるシートを詰めこんだ。The resulting gap between the upper lids was filled with a needle-punched sheet of polypropylene fibers.
そして下部のふたをしめ、水を8.0%程度入れ、上部
のふたをしめた。Then, the bottom lid was closed, approximately 8.0% water was added, and the top lid was closed.
使用するまでは、この状態で保管した。It was stored in this state until use.
ドラム缶を利用して、このカートリッジエレメントがセ
ット出来るハウジングを作成した。Using a drum can, we created a housing in which this cartridge element could be set.
その概要は第3図の通りである。The outline is shown in Figure 3.
ドラム缶19の底部に穴を開はジヨイント20からの排
出液がパイプ22を通じて排出されるようにした。A hole is made in the bottom of the drum can 19 so that the liquid discharged from the joint 20 can be discharged through a pipe 22.
上記のカートリッジエレメントをジヨイント20にワン
タッチではめこめば、内圧によってカートリッジエレメ
ントは、ジヨイントに圧着されてシールが完全になった
。When the above-mentioned cartridge element was fitted into the joint 20 with one touch, the cartridge element was crimped onto the joint by internal pressure and a complete seal was formed.
この装置を用いて処理したところ次の結果を得た。When this device was used for processing, the following results were obtained.
第1図は、本発明のフローシートの説明図であり、図中
主な符号として4は砂涙過塔、5は吸着塔である。
第2、図はカーt−IJツジユニットを用いた本発明の
詳細な説明図である。
符号10〜13はカートリッジユニットである。
第3図は、カートリッジエレメントを容器内にセットす
る方式の説明図である。FIG. 1 is an explanatory diagram of the flow sheet of the present invention, and in the figure, the main symbols 4 are a sand filter tower, and 5 is an adsorption tower. The second figure is a detailed explanatory diagram of the present invention using a cart t-IJ joint unit. Reference numerals 10 to 13 are cartridge units. FIG. 3 is an explanatory diagram of a method for setting a cartridge element in a container.
Claims (1)
を処理するに際し、水を予め砂濾過工程で処理し、次い
で吸着工程で処理すること、及び吸着工程で用いる吸着
材が処理対象物に対して物理的に活性能を有する物質と
一体化状態にある担体とから構成されている複合体であ
ることを特徴とする水の処理法。1. When treating water through a treatment process consisting of a sand filtration process and an adsorption process, the water is first treated in the sand filtration process and then in the adsorption process, and the adsorbent used in the adsorption process is 1. A method for treating water, characterized in that it is a complex composed of a substance having physical activity and a carrier in an integrated state.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP12454076A JPS5918111B2 (en) | 1976-10-18 | 1976-10-18 | Water treatment method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP12454076A JPS5918111B2 (en) | 1976-10-18 | 1976-10-18 | Water treatment method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5349854A JPS5349854A (en) | 1978-05-06 |
| JPS5918111B2 true JPS5918111B2 (en) | 1984-04-25 |
Family
ID=14887996
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP12454076A Expired JPS5918111B2 (en) | 1976-10-18 | 1976-10-18 | Water treatment method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5918111B2 (en) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6087888A (en) * | 1983-10-19 | 1985-05-17 | Shigemi Uchida | Waste water treating apparatus for gas station |
| NL1014497C2 (en) * | 2000-02-25 | 2001-08-28 | Moons & Van Hoof B V | Treating unpurified drinking, spring and/or rain water comprises filtering using at least one layer of zeolite-containing material |
| JP5180458B2 (en) | 2006-10-26 | 2013-04-10 | 三洋電機株式会社 | Water purification equipment |
| JP2008222978A (en) * | 2007-03-15 | 2008-09-25 | Mitsui Eng & Shipbuild Co Ltd | Charcoal gasifier |
-
1976
- 1976-10-18 JP JP12454076A patent/JPS5918111B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5349854A (en) | 1978-05-06 |
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