JP4658873B2 - Aggregation treatment agent and method for stabilizing aqueous solution of aggregation treatment agent - Google Patents
Aggregation treatment agent and method for stabilizing aqueous solution of aggregation treatment agent Download PDFInfo
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- 239000007864 aqueous solution Substances 0.000 title claims description 11
- 238000000034 method Methods 0.000 title claims description 10
- 230000000087 stabilizing effect Effects 0.000 title claims description 5
- 230000002776 aggregation Effects 0.000 title description 8
- 238000004220 aggregation Methods 0.000 title description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 48
- 229920000642 polymer Polymers 0.000 claims description 47
- 239000000243 solution Substances 0.000 claims description 39
- 239000003795 chemical substances by application Substances 0.000 claims description 27
- 239000000126 substance Substances 0.000 claims description 24
- 230000002378 acidificating effect Effects 0.000 claims description 23
- 230000004931 aggregating effect Effects 0.000 claims description 21
- 239000003638 chemical reducing agent Substances 0.000 claims description 21
- 239000008394 flocculating agent Substances 0.000 claims description 9
- 229920001577 copolymer Polymers 0.000 claims description 7
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- HRPVXLWXLXDGHG-UHFFFAOYSA-N Acrylamide Chemical compound NC(=O)C=C HRPVXLWXLXDGHG-UHFFFAOYSA-N 0.000 claims description 5
- LNOPIUAQISRISI-UHFFFAOYSA-N n'-hydroxy-2-propan-2-ylsulfonylethanimidamide Chemical compound CC(C)S(=O)(=O)CC(N)=NO LNOPIUAQISRISI-UHFFFAOYSA-N 0.000 claims description 5
- NIXOWILDQLNWCW-UHFFFAOYSA-M Acrylate Chemical compound [O-]C(=O)C=C NIXOWILDQLNWCW-UHFFFAOYSA-M 0.000 claims description 4
- CIWBSHSKHKDKBQ-JLAZNSOCSA-N Ascorbic acid Chemical compound OC[C@H](O)[C@H]1OC(=O)C(O)=C1O CIWBSHSKHKDKBQ-JLAZNSOCSA-N 0.000 claims description 4
- -1 dimethylaminoethyl Chemical group 0.000 claims description 4
- FQPSGWSUVKBHSU-UHFFFAOYSA-N methacrylamide Chemical compound CC(=C)C(N)=O FQPSGWSUVKBHSU-UHFFFAOYSA-N 0.000 claims description 4
- KDYFGRWQOYBRFD-UHFFFAOYSA-N succinic acid Chemical compound OC(=O)CCC(O)=O KDYFGRWQOYBRFD-UHFFFAOYSA-N 0.000 claims description 4
- 238000004065 wastewater treatment Methods 0.000 claims description 4
- 239000008235 industrial water Substances 0.000 claims description 3
- DHCDFWKWKRSZHF-UHFFFAOYSA-N sulfurothioic S-acid Chemical compound OS(O)(=O)=S DHCDFWKWKRSZHF-UHFFFAOYSA-N 0.000 claims description 3
- LSNNMFCWUKXFEE-UHFFFAOYSA-M Bisulfite Chemical compound OS([O-])=O LSNNMFCWUKXFEE-UHFFFAOYSA-M 0.000 claims description 2
- 239000002211 L-ascorbic acid Substances 0.000 claims description 2
- 235000000069 L-ascorbic acid Nutrition 0.000 claims description 2
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 claims description 2
- 229960005070 ascorbic acid Drugs 0.000 claims description 2
- 229920001519 homopolymer Polymers 0.000 claims description 2
- 230000006641 stabilisation Effects 0.000 claims 1
- 238000011105 stabilization Methods 0.000 claims 1
- 239000001384 succinic acid Substances 0.000 claims 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 21
- 229910052801 chlorine Inorganic materials 0.000 description 21
- 239000000460 chlorine Substances 0.000 description 21
- 230000007423 decrease Effects 0.000 description 19
- 238000004090 dissolution Methods 0.000 description 16
- 230000000052 comparative effect Effects 0.000 description 12
- 239000000178 monomer Substances 0.000 description 7
- 229920006317 cationic polymer Polymers 0.000 description 6
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 description 6
- 239000012535 impurity Substances 0.000 description 6
- 238000001704 evaporation Methods 0.000 description 5
- 230000008020 evaporation Effects 0.000 description 5
- 238000002360 preparation method Methods 0.000 description 5
- 239000000047 product Substances 0.000 description 5
- 239000010865 sewage Substances 0.000 description 5
- 238000003860 storage Methods 0.000 description 5
- VZCYOOQTPOCHFL-OWOJBTEDSA-N Fumaric acid Chemical compound OC(=O)\C=C\C(O)=O VZCYOOQTPOCHFL-OWOJBTEDSA-N 0.000 description 4
- WNLRTRBMVRJNCN-UHFFFAOYSA-N adipic acid Chemical compound OC(=O)CCCCC(O)=O WNLRTRBMVRJNCN-UHFFFAOYSA-N 0.000 description 4
- 239000003792 electrolyte Substances 0.000 description 4
- 238000003756 stirring Methods 0.000 description 4
- PQUXFUBNSYCQAL-UHFFFAOYSA-N 1-(2,3-difluorophenyl)ethanone Chemical compound CC(=O)C1=CC=CC(F)=C1F PQUXFUBNSYCQAL-UHFFFAOYSA-N 0.000 description 3
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 description 3
- 125000000129 anionic group Chemical group 0.000 description 3
- 125000002091 cationic group Chemical group 0.000 description 3
- 230000007062 hydrolysis Effects 0.000 description 3
- 238000006460 hydrolysis reaction Methods 0.000 description 3
- 230000003472 neutralizing effect Effects 0.000 description 3
- 229940047670 sodium acrylate Drugs 0.000 description 3
- AKHNMLFCWUSKQB-UHFFFAOYSA-L sodium thiosulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=S AKHNMLFCWUSKQB-UHFFFAOYSA-L 0.000 description 3
- 235000019345 sodium thiosulphate Nutrition 0.000 description 3
- VZSRBBMJRBPUNF-UHFFFAOYSA-N 2-(2,3-dihydro-1H-inden-2-ylamino)-N-[3-oxo-3-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)propyl]pyrimidine-5-carboxamide Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)C(=O)NCCC(N1CC2=C(CC1)NN=N2)=O VZSRBBMJRBPUNF-UHFFFAOYSA-N 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 229940048053 acrylate Drugs 0.000 description 2
- 239000001361 adipic acid Substances 0.000 description 2
- 235000011037 adipic acid Nutrition 0.000 description 2
- 238000005054 agglomeration Methods 0.000 description 2
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- KDYFGRWQOYBRFD-NUQCWPJISA-N butanedioic acid Chemical compound O[14C](=O)CC[14C](O)=O KDYFGRWQOYBRFD-NUQCWPJISA-N 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 239000007857 degradation product Substances 0.000 description 2
- 239000001530 fumaric acid Substances 0.000 description 2
- WQYVRQLZKVEZGA-UHFFFAOYSA-N hypochlorite Chemical compound Cl[O-] WQYVRQLZKVEZGA-UHFFFAOYSA-N 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 229910052751 metal Chemical class 0.000 description 2
- 239000002184 metal Chemical class 0.000 description 2
- 150000007522 mineralic acids Chemical class 0.000 description 2
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- SONHXMAHPHADTF-UHFFFAOYSA-M sodium;2-methylprop-2-enoate Chemical compound [Na+].CC(=C)C([O-])=O SONHXMAHPHADTF-UHFFFAOYSA-M 0.000 description 2
- 239000008399 tap water Substances 0.000 description 2
- 235000020679 tap water Nutrition 0.000 description 2
- VZCYOOQTPOCHFL-UHFFFAOYSA-N trans-butenedioic acid Natural products OC(=O)C=CC(O)=O VZCYOOQTPOCHFL-UHFFFAOYSA-N 0.000 description 2
- CERQOIWHTDAKMF-UHFFFAOYSA-N Methacrylic acid Chemical compound CC(=C)C(O)=O CERQOIWHTDAKMF-UHFFFAOYSA-N 0.000 description 1
- 230000004075 alteration Effects 0.000 description 1
- 150000001408 amides Chemical class 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000000701 coagulant Substances 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 238000013329 compounding Methods 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 238000010494 dissociation reaction Methods 0.000 description 1
- 230000005593 dissociations Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005189 flocculation Methods 0.000 description 1
- 230000016615 flocculation Effects 0.000 description 1
- 125000000524 functional group Chemical group 0.000 description 1
- 229940093915 gynecological organic acid Drugs 0.000 description 1
- 239000010800 human waste Substances 0.000 description 1
- 150000002429 hydrazines Chemical class 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 235000005985 organic acids Nutrition 0.000 description 1
- ACVYVLVWPXVTIT-UHFFFAOYSA-M phosphinate Chemical compound [O-][PH2]=O ACVYVLVWPXVTIT-UHFFFAOYSA-M 0.000 description 1
- 229920000058 polyacrylate Polymers 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 230000009257 reactivity Effects 0.000 description 1
- FWFUWXVFYKCSQA-UHFFFAOYSA-M sodium;2-methyl-2-(prop-2-enoylamino)propane-1-sulfonate Chemical compound [Na+].[O-]S(=O)(=O)CC(C)(C)NC(=O)C=C FWFUWXVFYKCSQA-UHFFFAOYSA-M 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 230000001954 sterilising effect Effects 0.000 description 1
- 238000004659 sterilization and disinfection Methods 0.000 description 1
- 229920001897 terpolymer Polymers 0.000 description 1
- FZGFBJMPSHGTRQ-UHFFFAOYSA-M trimethyl(2-prop-2-enoyloxyethyl)azanium;chloride Chemical compound [Cl-].C[N+](C)(C)CCOC(=O)C=C FZGFBJMPSHGTRQ-UHFFFAOYSA-M 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Landscapes
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Description
本発明は、溶解液が安定な凝集処理剤に関し、詳しくは高分子凝集剤、還元剤および該高分子凝集剤を0.1質量%以上に溶解した場合の溶解液pHを6以下にする量の酸性物質の三成分を組み合わせることによる溶解液が安定な凝集処理剤に関する。また前記凝集処理剤を溶解するに際し、溶解水に還元剤および酸性物質で処理した後、高分子凝集剤を溶解するか、あるいは高分子凝集剤、還元剤および酸性物質を同時に溶解することによる高分子凝集剤溶解液の安定化方法にも関する。 The present invention relates to a flocculating agent having a stable solution, and more specifically, a polymer flocculant, a reducing agent, and an amount that makes the solution pH 6 or less when the polymer flocculant is dissolved in 0.1% by mass or more. The present invention relates to an aggregating treatment agent in which a solution is stable by combining three components of acidic substances. Further, when dissolving the aggregating agent, after treating with a reducing agent and an acidic substance in dissolved water, the polymer aggregating agent is dissolved, or the polymer aggregating agent, the reducing agent and the acidic substance are dissolved at the same time. It also relates to a method for stabilizing a molecular flocculant solution.
粉末状高分子凝集剤を下水処理、し尿処理、産業廃水処理、その他の廃水処理に用いる場合、溶解槽で溶解水を用いて溶解し、通常0.1〜0.3%濃度の溶解液とし、これを処理槽に添加する。通常、溶解水はコストの関係から工業用水、河川水、処理水(水処理後の再生水)等が用いられるが、溶解液の性状は溶解水の水質、特に含まれる残留塩素、電解質等の不純物に大きく依存し、これらの種類および濃度によってはイオン性官能基の解離が阻害され、粘度低下や経時的な劣化を起こし、それが凝集性能に影響するという問題点を含んでいる。廃水処理施設では、溶解水として特に処理水を用いる場合が多いが、処理水は塩素殺菌などによる残留塩素や金属塩を含む場合が多い。このため、処理水に限らず、溶解水中の残留塩素、電解質、その他不純物の濃度によって、粘度の低下した溶解液が得られ、全く粘性を示さない溶液が得られる場合もあり、高分子凝集剤の凝集性能を大きく低下させる。また、多くの場合、溶解液調製後、不純物やpHなどの影響を受け、高分子凝集剤の変質や分解による分子量低下が起こり、さらに高分子凝集剤が加水分解により経時的に劣化し、溶解液の粘度低下が進むという問題点もある。このため高分子凝集剤溶解液の作り置きが出来ず、調製後は出来るだけ早く使用しなければならないという不便さがある。 When the powdery polymer flocculant is used for sewage treatment, human waste treatment, industrial wastewater treatment, and other wastewater treatment, it is dissolved using dissolution water in a dissolution tank, and is usually made into a 0.1 to 0.3% concentration solution. This is added to the treatment tank. Normally, industrial water, river water, treated water (reclaimed water after water treatment), etc. are used as dissolved water because of cost, but the properties of the dissolved liquid are the quality of the dissolved water, especially impurities such as residual chlorine and electrolytes. Depending on the type and concentration, dissociation of the ionic functional group is inhibited, resulting in a decrease in viscosity and deterioration over time, which affects the aggregation performance. In wastewater treatment facilities, treated water is often used as dissolved water, but the treated water often contains residual chlorine and metal salts resulting from chlorine sterilization. For this reason, not only treated water but also a solution with reduced viscosity may be obtained depending on the concentration of residual chlorine, electrolyte and other impurities in the dissolved water, and a solution having no viscosity may be obtained. The agglomeration performance is greatly reduced. Also, in many cases, after preparation of the solution, it is affected by impurities, pH, etc., resulting in a decrease in molecular weight due to alteration or decomposition of the polymer flocculant. There is also a problem in that the viscosity of the liquid decreases. For this reason, there is an inconvenience that a polymer flocculant solution cannot be prepared and must be used as soon as possible after preparation.
以上のように、高分子凝集剤溶解液は、高分子凝集剤溶解時の粘度低下と溶解液調製後の貯蔵時における経時的な粘度低下という問題点を含んでいる。後者の加水分解による経時的な粘度低下を抑制する方法としては、溶解液に酸を加えて、水溶液を酸性領域にする方法が提案されている(特許文献1、2)。しかしながら、これらの方法は溶解時点での粘度低下には対応できない。
上述の通り、高分子凝集剤溶解液の性状は、その溶解水の性状に大きく依存し、溶解水に含まれる残留塩素、電解質やその他不純物によって低粘度の溶解液が得られ、さらに経時的に粘度が低下するという問題点を有している。例えば、次亜塩素酸塩で殺菌を行い、残留塩素を多く含有する水の場合には、特に溶解時の粘度低下が激しく、残留塩素濃度によっては、溶解液がほとんど粘性を示さない場合もある。この溶解時の粘度低下は残留塩素、不純物イオンによる高分子凝集剤の反応性の低下や分解により起こり、経時的な粘度低下は主として高分子凝集剤の加水分解によるものと考えられ、この発明では、これらの問題を解決し、正常で安定な凝集性能を発揮する高分子凝集剤および溶解液の安定化方法を提供することを目的とする。 As described above, the properties of the polymer flocculant solution greatly depend on the properties of the dissolved water, and a low-viscosity solution can be obtained by residual chlorine, electrolytes and other impurities contained in the dissolved water. There is a problem that the viscosity decreases. For example, in the case of water sterilized with hypochlorite and containing a lot of residual chlorine, the viscosity decreases particularly during dissolution, and depending on the residual chlorine concentration, the solution may not exhibit any viscosity. . This decrease in viscosity at the time of dissolution is caused by a decrease in the reactivity and decomposition of the polymer flocculant due to residual chlorine and impurity ions. An object of the present invention is to solve these problems and to provide a polymer flocculant that exhibits normal and stable flocculation performance and a method for stabilizing a solution.
本発明者らは、上記課題を解決するために鋭意検討を行った結果、高分子凝集剤、還元剤および該高分子凝集剤を0.1質量%以上に溶解した場合の溶解液pHを6以下にする量の酸性物質の三成分を組み合わせたことからなる凝集処理剤を溶解した場合、高分子凝集剤の溶解時点での粘度低下を抑制し、さらに貯蔵時の経時的な粘度低下を抑制できる安定な水溶液が得られることを発見し本発明に達した。 As a result of intensive studies to solve the above problems, the present inventors have determined that the solution pH when the polymer flocculant, the reducing agent, and the polymer flocculant are dissolved in 0.1% by mass or more is 6%. When a coagulation treatment agent consisting of a combination of the three components of acidic substances in the following amount is dissolved, the viscosity decrease at the time of dissolution of the polymer coagulant is suppressed, and further the viscosity decrease over time during storage is suppressed. It was discovered that a stable aqueous solution was obtained and the present invention was reached.
また前記凝集処理剤は、高分子凝集剤、還元剤および酸性物質からなる粉末状あるいは顆粒状の混合物であることが好ましい。 The aggregating agent is preferably a powdery or granular mixture comprising a polymer aggregating agent, a reducing agent and an acidic substance.
また本発明は、前記凝集処理剤が溶解水に溶解して水溶液とするに際し、溶解水に前記還元剤と前記高分子凝集剤を0.1質量%以上に溶解した場合の溶解液pHを6以下にする量の酸性物質を溶解した後、前記高分子凝集剤を溶解するか、あるいは高分子凝集剤、還元剤および酸性物質を同時に溶解すると安定な凝集処理剤水溶液が得られることを特徴とする凝集処理剤水溶液の安定化方法にも関する。 In the present invention, when the aggregating agent is dissolved in dissolved water to form an aqueous solution, the solution pH when the reducing agent and the polymer aggregating agent are dissolved in 0.1% by mass or more in dissolved water is 6 It is characterized in that a stable aggregating agent aqueous solution can be obtained by dissolving the polymer flocculant after dissolving the amount of acidic substance to be described below, or by dissolving the polymer flocculant, the reducing agent and the acidic substance at the same time. The present invention also relates to a method for stabilizing an aggregating agent aqueous solution.
高分子凝集剤水溶液は、溶解水に含まれる残留塩素、電解質、その他不純物の影響により、溶液中の高分子凝集剤が加水分解等の変性を受け、溶解時の粘度低下や経時的な粘度低下を起こし、正常な凝集性能を発揮できなくなる。この問題点を解決するため本発明は以下の方法を提供するものである。すなわち本発明は、高分子凝集剤、還元剤および該高分子凝集剤を0.1質量%以上に溶解した場合の溶解液pHを6以下にする量の酸性物質の三成分を組み合わせることからなる凝集処理剤である。 The polymer flocculant aqueous solution is affected by the residual chlorine, electrolyte, and other impurities contained in the dissolved water, and the polymer flocculant in the solution undergoes modification such as hydrolysis, resulting in a decrease in viscosity during dissolution and a decrease in viscosity over time. Cause normal agglomeration performance. In order to solve this problem, the present invention provides the following method. That is, the present invention comprises a combination of a polymer flocculant, a reducing agent, and three components of an acidic substance in an amount that makes the solution pH 6 or less when the polymer flocculant is dissolved in 0.1% by mass or more. It is an aggregating agent.
本発明の凝集処理剤は、高分子凝集剤、還元剤および該高分子凝集剤を0.1質量%以上に溶解した場合の溶解液pHを6以下にする量の酸性物質からなる粉末状あるいは顆粒状の混合物にすることができる。該還元剤は、溶解水中の残留塩素を中和還元する性状を有するため、また該酸は高分子凝集剤の加水分解を抑制するため水溶液の安定性を向上させることができる。 The aggregating agent of the present invention is a powdery substance comprising an acidic substance in an amount that makes the solution pH 6 or less when the polymer flocculant, the reducing agent and the polymer flocculant are dissolved in 0.1% by mass or more. It can be a granular mixture. Since the reducing agent has a property of neutralizing and reducing residual chlorine in the dissolved water, and the acid suppresses hydrolysis of the polymer flocculant, the stability of the aqueous solution can be improved.
また本発明の凝集処理剤は、溶解水に溶解して水溶液とするに際し、溶解水に前記還元剤と前記高分子凝集剤を0.1質量%以上に溶解した場合の溶解液pHを6以下にする量の酸性物質を溶解した後、前記高分子凝集剤を溶解するか、あるいは前記高分子凝集剤、前記還元剤および前記酸性物質を同時に溶解することによって凝集処理剤水溶液を安定化することができる。 In addition, when the aggregating agent of the present invention is dissolved in dissolved water to form an aqueous solution, the solution pH when the reducing agent and the polymer aggregating agent are dissolved in 0.1% by mass or more in dissolved water is 6 or less. After the amount of the acidic substance to be dissolved is dissolved, the polymer flocculant is dissolved, or the polymer flocculant, the reducing agent, and the acidic substance are dissolved simultaneously to stabilize the aqueous flocculating agent solution. Can do.
本発明で使用する還元剤は、以下のようなものである。すなわちチオ硫酸塩、亜硫酸塩、重亜硫酸塩、次亜リン酸塩、L−アスコルビン酸またはその塩、あるいはヒドラジン類などである。これらから選択される一種あるいは二種以上の組み合わせである。これら還元剤は、溶解水中の残留塩素を中和還元する性状を有するため、溶解水の性状、特に残留塩素濃度によって異なるが、溶解水に対して、通常5〜500pppmとなる量を添加することによって、その効果を発揮する。この中では、チオ硫酸塩が溶解水中の残留塩素を中和還元し、さらに金属類を取り込む性状を有するため、特に好ましい。これら還元剤の添加量として、高分子凝集剤、還元剤、酸性物質を逐次添加し溶解する場合は、対溶解水0.0005〜0.01質量%であり、好ましくは0.001〜0.005質量%である。また粉末状あるいは顆粒状の混合物として製品を調製する場合は、対高分子凝集剤0.5〜5質量%であり、好ましくは0.5〜2質量%である。 The reducing agent used in the present invention is as follows. That is, thiosulfate, sulfite, bisulfite, hypophosphite, L-ascorbic acid or a salt thereof, or hydrazines. One or a combination of two or more selected from these. Since these reducing agents have the property of neutralizing and reducing residual chlorine in the dissolved water, the amount of water that is usually 5 to 500 pppm is added to the dissolved water, although it varies depending on the properties of the dissolved water, particularly the residual chlorine concentration. To exert its effect. Of these, thiosulfate is particularly preferred because it has the property of neutralizing and reducing residual chlorine in dissolved water and further incorporating metals. When the polymer flocculant, the reducing agent, and the acidic substance are sequentially added and dissolved as the addition amount of these reducing agents, the amount is 0.0005 to 0.01% by mass with respect to the dissolved water, preferably 0.001 to 0.00. 005% by mass. Moreover, when preparing a product as a powdery or granular mixture, it is 0.5-5 mass% with respect to a polymer flocculent, Preferably it is 0.5-2 mass%.
また酸性物質は高分子凝集剤を0.1質量%以上に溶解した場合の溶解液pHを6以下にする量の酸性物質である。このような酸性物質の例として、無機あるいは有機の酸として塩酸、硫酸、酢酸、
スルファミン酸、クエン酸、フマル酸、コハク酸、アジピン酸などである。また本発明の凝集処理剤は、高分子凝集剤、酸性物質および還元剤の三成分を含有する粉末状あるいは顆粒状の製品形態にすることが可能である。その場合は固体状の無機あるいは有機の酸が好ましく、スルファミン酸、クエン酸、フマル酸、コハク酸、アジピン酸などが好ましい。これら酸性物質の添加量として、高分子凝集剤、還元剤、酸性物質を逐次添加し溶解する場合は、対溶解水0.001〜0.01質量%であり、好ましくは0.001〜0.005質量%である。また粉末状あるいは顆粒状の混合物として製品を調製する場合は、対高分子凝集剤0.1〜10質量%であり、好ましくは0.5〜5質量%である。
Moreover, an acidic substance is an acidic substance of the quantity which makes the solution pH 6 or less at the time of melt | dissolving a polymer flocculent in 0.1 mass% or more. Examples of such acidic substances include hydrochloric acid, sulfuric acid, acetic acid, inorganic or organic acids,
Sulfamic acid, citric acid, fumaric acid, succinic acid, adipic acid and the like. Further, the flocculating agent of the present invention can be made into a powdery or granular product form containing three components of a polymer flocculating agent, an acidic substance and a reducing agent. In that case, a solid inorganic or organic acid is preferable, and sulfamic acid, citric acid, fumaric acid, succinic acid, adipic acid and the like are preferable. The amount of these acidic substances to be added is 0.001 to 0.01% by mass with respect to the dissolved water, preferably 0.001 to 0.005%, when a polymer flocculant, a reducing agent, and an acidic substance are sequentially added and dissolved. 005% by mass. Moreover, when preparing a product as a powdery or granular mixture, it is 0.1-10 mass% with respect to a polymer flocculent, Preferably it is 0.5-5 mass%.
本発明で使用する高分子凝集剤は、カチオン性高分子凝集剤、アニオン性高分子凝集剤、両性高分子凝集剤のいずれでも良い。カチオン性高分子凝集剤としては、ジメチルアミノエチル(メタ)アクリレート、ジメチルアミノプロピル(メタ)アクリレートまたはそれらの4級塩もしくは3級塩の単独重合物、あるいはそれらとアクリルアミドまたはメタクリルアミドとの共重合物、ポリアクリルアミドまたはポリメタクリルアミドのホフマン分解物、ポリアミジンなどが挙げられるが、これらに限定されない。アニオン系高分子凝集剤としては、アクリル酸ナトリウム重合物、アクリル酸ナトリウムまたはメタクリル酸ナトリウムとアクリルアミドまたはメタクリルアミドとの共重合物、アクリルアミド重合物またはメタクリルアミド重合物の部分加水分解物、アクリルアミドまたはメタクリルアミドとアクリル酸ナトリウムまたはメタクリル酸ナトリウムと2−アクリルアミド−2−メチルプロパンスルホン酸ナトリウムの三元共重合物などが挙げられるが、これらに限定されない。両性高分子凝集剤としては、アニオン性モノマーとカチオン性モノマーの共重合物、アニオン性モノマーとカチオン性モノマーとノニオン性モノマーの共重合物、あるいはアニオン性モノマーとカチオン性モノマーの共重合物のマンニッヒ変性物またはホフマン分解物などが挙げられるが、これらに限定されない。 The polymer flocculant used in the present invention may be any of a cationic polymer flocculant, an anionic polymer flocculant, and an amphoteric polymer flocculant. Examples of cationic polymer flocculants include dimethylaminoethyl (meth) acrylate, dimethylaminopropyl (meth) acrylate, homopolymers of quaternary salts or tertiary salts thereof, and copolymers thereof with acrylamide or methacrylamide. Products, polyacrylamide or polymethacrylamide Hoffman degradation products, polyamidine, and the like. Anionic polymer flocculants include sodium acrylate polymer, copolymer of sodium acrylate or sodium methacrylate and acrylamide or methacrylamide, partial hydrolyzate of acrylamide polymer or methacrylamide polymer, acrylamide or methacrylic acid. Examples include, but are not limited to, terpolymers of amide and sodium acrylate or sodium methacrylate and sodium 2-acrylamido-2-methylpropanesulfonate. Amphoteric polymer flocculants include anionic monomer and cationic monomer copolymer, anionic monomer, cationic monomer and nonionic monomer copolymer, or anionic monomer and cationic monomer copolymer Mannich. Examples include, but are not limited to, denatured products or Hoffman degradation products.
溶解水としては、通常、溶解水として用いられる全ての水が対象であり、具体的には廃水処理した処理水、工業用水、河川水、水道水等が挙げられる。特に塩素殺菌した残留塩素を含む処理水に対して大きく効果を発揮する。 The dissolved water is usually all water used as dissolved water, and specifically includes treated water treated with waste water, industrial water, river water, tap water, and the like. It is particularly effective for treated water containing residual chlorine that has been sterilized with chlorine.
(実施例)以下に実施例および比較例を挙げて本発明をさらに具体的に説明するが、本発明はこれらの例によって限定されるものではない。 EXAMPLES The present invention will be described more specifically with reference to the following examples and comparative examples. However, the present invention is not limited to these examples.
溶解水として下水処理場における処理水(残留塩素:1.8mg/l、蒸発残留物 :980mg/l)を用い、その500mlにカチオン性高分子凝集剤(アクリロルオキシエチルトリメチルアンモニウムクロリド60モル%、アクリルアミド40モル%共重合物、分子量700万)1gとチオ硫酸ナトリウムを表1に記載した質量%加え、攪拌下に1時間溶解処理を行う。得られた溶解液に表1に記載したpHになるようスルファミン酸を加えた。この溶解液を室温に放置し、溶解直後、2時間後、8時間後、24時間後、72時間後の計5回サンプリングし、それぞれの粘度を測定する。結果を表1に示す。 Treated water in a sewage treatment plant (residual chlorine: 1.8 mg / l, evaporation residue: 980 mg / l) was used as dissolved water, and a cationic polymer flocculant (acryloyloxyethyltrimethylammonium chloride 60 mol%) in 500 ml thereof. 1 g of acrylamide 40 mol% copolymer, molecular weight 7 million) and sodium thiosulfate in mass% listed in Table 1 are added, and dissolution treatment is performed with stirring for 1 hour. Sulfamic acid was added to the resulting solution so as to have the pH described in Table 1. This solution is allowed to stand at room temperature, sampled 5 times in total, immediately after dissolution, 2 hours, 8 hours, 24 hours and 72 hours, and the respective viscosities are measured. The results are shown in Table 1.
(比較例1)溶解水として水道水(残留塩素:0.7mg/l、蒸発残留物:122mg/l)を用い、その500mlに実施例で用いたと同様なカチオン性高分子凝集剤1gを加え、攪拌下に1時間溶解処理を行う。得られた溶解液のpHは6.5である。この溶解液を室温に放置し、溶解直後、2時間後、8時間後、24時間後、72時間後の計5回サンプリングし、それぞれの粘度を測定する。結果を表1に示す。 (Comparative Example 1) Tap water (residual chlorine: 0.7 mg / l, evaporation residue: 122 mg / l) was used as dissolved water, and 1 g of a cationic polymer flocculant similar to that used in the example was added to 500 ml thereof. The dissolution treatment is performed for 1 hour under stirring. The pH of the resulting solution is 6.5. This solution is allowed to stand at room temperature, sampled 5 times in total, immediately after dissolution, 2 hours, 8 hours, 24 hours, and 72 hours, and the respective viscosities are measured. The results are shown in Table 1.
(比較例2)溶解水として実施例で用いたものと同じ下水処理場における処理水(残留塩素:1.8mg/l、蒸発残留物 :980mg/l)を用い、その500mlに比較例1と同様のカチオン性高分子凝集剤1gを加え、攪拌下に1時間溶解処理を行う。得られた溶解液のpHは6.6である。この溶解液を室温に放置し、溶解直後、2時間後、8時間後、24時間後、72時間後の計5回サンプリングし、それぞれの粘度を測定する。結果を表1に示す。 (Comparative Example 2) Using treated water (residual chlorine: 1.8 mg / l, evaporation residue: 980 mg / l) in the same sewage treatment plant as used in Examples as dissolved water, 500 ml thereof was compared with Comparative Example 1 1 g of the same cationic polymer flocculant is added, and dissolution treatment is performed for 1 hour with stirring. The pH of the resulting solution is 6.6. This solution is allowed to stand at room temperature, sampled 5 times in total, immediately after dissolution, 2 hours, 8 hours, 24 hours, and 72 hours, and the respective viscosities are measured. The results are shown in Table 1.
(比較例3)溶解水として下水処理場Aにおける処理水(残留塩素:1.8mg/l、蒸発残留物 :980mg/l)を用い、その500mlに比較例1と同様のカチオン性高分子凝集剤1gとチオ硫酸ナトリウムを表1に記載した質量%加え、攪拌下に1時間溶解処理を行う。得られた溶解液のpHは6.4である。この溶解液を室温に放置し、溶解直後、2時間後、8時間後、24時間後、72時間後の計5回サンプリングし、それぞれの粘度を測定する。結果を表1に示す。 (Comparative Example 3) Treated water in the sewage treatment plant A (residual chlorine: 1.8 mg / l, evaporation residue: 980 mg / l) was used as dissolved water, and 500 ml of the same cationic polymer agglomerates as in Comparative Example 1 1 g of the agent and sodium thiosulfate in mass% described in Table 1 are added, and dissolution treatment is performed for 1 hour with stirring. The pH of the resulting solution is 6.4. This solution is allowed to stand at room temperature, sampled 5 times in total, immediately after dissolution, 2 hours, 8 hours, 24 hours, and 72 hours, and the respective viscosities are measured. The results are shown in Table 1.
表より比較例1では、溶解直後は高い粘度を示すが、その後徐々に経時的に粘度低下が進むことが分かる。また比較例2では、初期粘度が極めて低く、しかも経時的粘度低下が大きいことが分かる。さらに比較例3では、初期粘度が低く、経時的粘度低下が大きいことが分かる。これらに対し本発明の凝集処理剤では、72時間後でも粘度低下が小さいことが分かる。 From the table, it can be seen that Comparative Example 1 shows a high viscosity immediately after dissolution, but then gradually decreases in viscosity over time. In Comparative Example 2, it can be seen that the initial viscosity is extremely low and the viscosity decrease with time is large. Furthermore, in Comparative Example 3, it can be seen that the initial viscosity is low and the viscosity decrease with time is large. In contrast, it can be seen that the aggregation treatment agent of the present invention has a small decrease in viscosity even after 72 hours.
(表1)溶解液の経時的粘度変化
RCl;残留塩素量、STS;チオ硫酸ナトリウム添加量、SA;スルファミン酸、pH;調製後pH、
(Table 1) Change in viscosity of solution over time
RCl: amount of residual chlorine, STS: amount of sodium thiosulfate added, SA: sulfamic acid, pH: pH after preparation,
(粉末からなる凝集処理剤の調製と溶解液保存試験)表2に記載した質量%で各成分を配合して粉末状凝集処理剤を調製した。またこれら粉末状凝集処理剤を実施例1と同様に溶解水として下水処理場Aにおける処理水(残留塩素:1.8mg/l、蒸発残留物 :980mg/l)を用い0.2質量%に溶解し、経過時間ごとに溶液粘度を測定した。高分子凝集剤組成と配合比を表2に、溶解液保存試験の結果を表3に示す。 (Preparation of Aggregation Treatment Agent Containing Powder and Solution Storage Test) A powdery aggregation treatment agent was prepared by blending each component in mass% described in Table 2. In addition, these powdery flocculating agents were dissolved in the same manner as in Example 1 using treated water in sewage treatment plant A (residual chlorine: 1.8 mg / l, evaporation residue: 980 mg / l) to 0.2% by mass. It melt | dissolved and measured the solution viscosity for every elapsed time. Table 2 shows the polymer flocculant composition and blending ratio, and Table 3 shows the results of the solution storage test.
(比較例4)比較試料―1および比較試料―2に関しても同様な溶解液保存試験を実施した。その結果を表3に示す。 (Comparative Example 4) A similar solution storage test was conducted for Comparative Sample-1 and Comparative Sample-2. The results are shown in Table 3.
(表2)
高分子凝集剤化学組成;モル%、配合比;質量%
(Table 2)
Polymer flocculant chemical composition; mol%, compounding ratio; mass%
(表3)
(Table 3)
Claims (4)
The method for stabilizing an aggregating agent aqueous solution according to claim 3 , wherein the dissolved water is at least one selected from industrial water, river water, and treated water after wastewater treatment.
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