JP2008238131A - Water cleaning agent - Google Patents
Water cleaning agent Download PDFInfo
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- JP2008238131A JP2008238131A JP2007086228A JP2007086228A JP2008238131A JP 2008238131 A JP2008238131 A JP 2008238131A JP 2007086228 A JP2007086228 A JP 2007086228A JP 2007086228 A JP2007086228 A JP 2007086228A JP 2008238131 A JP2008238131 A JP 2008238131A
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- Prior art keywords
- water
- purification agent
- water purification
- ammonia
- fish
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 146
- 229910001868 water Inorganic materials 0.000 title claims abstract description 146
- 239000012459 cleaning agent Substances 0.000 title abstract 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims abstract description 110
- 229910021529 ammonia Inorganic materials 0.000 claims abstract description 55
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 34
- IOVCWXUNBOPUCH-UHFFFAOYSA-N Nitrous acid Chemical compound ON=O IOVCWXUNBOPUCH-UHFFFAOYSA-N 0.000 claims abstract description 33
- 239000011230 binding agent Substances 0.000 claims abstract description 12
- 150000001875 compounds Chemical class 0.000 claims abstract description 12
- 239000000843 powder Substances 0.000 claims abstract description 8
- 230000000737 periodic effect Effects 0.000 claims abstract description 7
- 238000000746 purification Methods 0.000 claims description 35
- 238000000034 method Methods 0.000 claims description 24
- VTHJTEIRLNZDEV-UHFFFAOYSA-L magnesium dihydroxide Chemical compound [OH-].[OH-].[Mg+2] VTHJTEIRLNZDEV-UHFFFAOYSA-L 0.000 claims description 11
- 239000000347 magnesium hydroxide Substances 0.000 claims description 11
- 229910001862 magnesium hydroxide Inorganic materials 0.000 claims description 11
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 claims description 7
- 239000000292 calcium oxide Substances 0.000 claims description 5
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 claims description 5
- 239000000395 magnesium oxide Substances 0.000 claims description 5
- 239000001856 Ethyl cellulose Substances 0.000 claims description 4
- ZZSNKZQZMQGXPY-UHFFFAOYSA-N Ethyl cellulose Chemical group CCOCC1OC(OC)C(OCC)C(OCC)C1OC1C(O)C(O)C(OC)C(CO)O1 ZZSNKZQZMQGXPY-UHFFFAOYSA-N 0.000 claims description 4
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims description 4
- 239000000920 calcium hydroxide Substances 0.000 claims description 4
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims description 4
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 claims description 4
- 229920002678 cellulose Polymers 0.000 claims description 4
- 239000001913 cellulose Substances 0.000 claims description 4
- 235000010980 cellulose Nutrition 0.000 claims description 4
- 235000019325 ethyl cellulose Nutrition 0.000 claims description 4
- 229920001249 ethyl cellulose Polymers 0.000 claims description 4
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical group [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 claims description 4
- 229920000609 methyl cellulose Polymers 0.000 claims description 4
- 239000001923 methylcellulose Substances 0.000 claims description 4
- 235000010981 methylcellulose Nutrition 0.000 claims description 4
- LNAZSHAWQACDHT-XIYTZBAFSA-N (2r,3r,4s,5r,6s)-4,5-dimethoxy-2-(methoxymethyl)-3-[(2s,3r,4s,5r,6r)-3,4,5-trimethoxy-6-(methoxymethyl)oxan-2-yl]oxy-6-[(2r,3r,4s,5r,6r)-4,5,6-trimethoxy-2-(methoxymethyl)oxan-3-yl]oxyoxane Chemical compound CO[C@@H]1[C@@H](OC)[C@H](OC)[C@@H](COC)O[C@H]1O[C@H]1[C@H](OC)[C@@H](OC)[C@H](O[C@H]2[C@@H]([C@@H](OC)[C@H](OC)O[C@@H]2COC)OC)O[C@@H]1COC LNAZSHAWQACDHT-XIYTZBAFSA-N 0.000 claims description 3
- IXPNQXFRVYWDDI-UHFFFAOYSA-N 1-methyl-2,4-dioxo-1,3-diazinane-5-carboximidamide Chemical compound CN1CC(C(N)=N)C(=O)NC1=O IXPNQXFRVYWDDI-UHFFFAOYSA-N 0.000 claims description 3
- 229920001479 Hydroxyethyl methyl cellulose Polymers 0.000 claims description 3
- 239000004372 Polyvinyl alcohol Substances 0.000 claims description 3
- HDSBZMRLPLPFLQ-UHFFFAOYSA-N Propylene glycol alginate Chemical compound OC1C(O)C(OC)OC(C(O)=O)C1OC1C(O)C(O)C(C)C(C(=O)OCC(C)O)O1 HDSBZMRLPLPFLQ-UHFFFAOYSA-N 0.000 claims description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 3
- 239000004115 Sodium Silicate Substances 0.000 claims description 3
- DPXJVFZANSGRMM-UHFFFAOYSA-N acetic acid;2,3,4,5,6-pentahydroxyhexanal;sodium Chemical compound [Na].CC(O)=O.OCC(O)C(O)C(O)C(O)C=O DPXJVFZANSGRMM-UHFFFAOYSA-N 0.000 claims description 3
- 239000001768 carboxy methyl cellulose Substances 0.000 claims description 3
- 239000008119 colloidal silica Substances 0.000 claims description 3
- 229920001577 copolymer Polymers 0.000 claims description 3
- 239000001866 hydroxypropyl methyl cellulose Substances 0.000 claims description 3
- 235000010979 hydroxypropyl methyl cellulose Nutrition 0.000 claims description 3
- 229920003088 hydroxypropyl methyl cellulose Polymers 0.000 claims description 3
- UFVKGYZPFZQRLF-UHFFFAOYSA-N hydroxypropyl methyl cellulose Chemical compound OC1C(O)C(OC)OC(CO)C1OC1C(O)C(O)C(OC2C(C(O)C(OC3C(C(O)C(O)C(CO)O3)O)C(CO)O2)O)C(CO)O1 UFVKGYZPFZQRLF-UHFFFAOYSA-N 0.000 claims description 3
- 229920001495 poly(sodium acrylate) polymer Polymers 0.000 claims description 3
- 229920002451 polyvinyl alcohol Polymers 0.000 claims description 3
- 235000010409 propane-1,2-diol alginate Nutrition 0.000 claims description 3
- 239000000770 propane-1,2-diol alginate Substances 0.000 claims description 3
- 235000010413 sodium alginate Nutrition 0.000 claims description 3
- 239000000661 sodium alginate Substances 0.000 claims description 3
- 229940005550 sodium alginate Drugs 0.000 claims description 3
- NNMHYFLPFNGQFZ-UHFFFAOYSA-M sodium polyacrylate Chemical compound [Na+].[O-]C(=O)C=C NNMHYFLPFNGQFZ-UHFFFAOYSA-M 0.000 claims description 3
- NTHWMYGWWRZVTN-UHFFFAOYSA-N sodium silicate Chemical compound [Na+].[Na+].[O-][Si]([O-])=O NTHWMYGWWRZVTN-UHFFFAOYSA-N 0.000 claims description 3
- 229910052911 sodium silicate Inorganic materials 0.000 claims description 3
- 229920003109 sodium starch glycolate Polymers 0.000 claims description 3
- 229940079832 sodium starch glycolate Drugs 0.000 claims description 3
- 239000008109 sodium starch glycolate Substances 0.000 claims description 3
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims description 2
- 229920002153 Hydroxypropyl cellulose Polymers 0.000 claims description 2
- 229910019142 PO4 Inorganic materials 0.000 claims description 2
- 239000011575 calcium Substances 0.000 claims description 2
- 229910052791 calcium Inorganic materials 0.000 claims description 2
- 235000001465 calcium Nutrition 0.000 claims description 2
- 238000004090 dissolution Methods 0.000 claims description 2
- 239000001863 hydroxypropyl cellulose Substances 0.000 claims description 2
- 235000010977 hydroxypropyl cellulose Nutrition 0.000 claims description 2
- 239000010452 phosphate Substances 0.000 claims description 2
- 235000019812 sodium carboxymethyl cellulose Nutrition 0.000 claims description 2
- 229920001027 sodium carboxymethylcellulose Polymers 0.000 claims description 2
- 229940080313 sodium starch Drugs 0.000 claims description 2
- 239000003232 water-soluble binding agent Substances 0.000 claims description 2
- 229920002134 Carboxymethyl cellulose Polymers 0.000 claims 1
- 235000010948 carboxy methyl cellulose Nutrition 0.000 claims 1
- 239000008112 carboxymethyl-cellulose Substances 0.000 claims 1
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 claims 1
- 241000251468 Actinopterygii Species 0.000 abstract description 54
- 229920003023 plastic Polymers 0.000 abstract description 12
- 230000006866 deterioration Effects 0.000 abstract description 6
- -1 etc. Substances 0.000 abstract description 6
- 239000008187 granular material Substances 0.000 abstract description 4
- 239000008235 industrial water Substances 0.000 abstract description 4
- 238000000465 moulding Methods 0.000 abstract description 4
- 239000010865 sewage Substances 0.000 abstract description 4
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 18
- 239000001569 carbon dioxide Substances 0.000 description 9
- 229910002092 carbon dioxide Inorganic materials 0.000 description 9
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 8
- 239000000460 chlorine Substances 0.000 description 8
- 229910052801 chlorine Inorganic materials 0.000 description 8
- 238000005259 measurement Methods 0.000 description 7
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 6
- 238000009434 installation Methods 0.000 description 6
- 244000005700 microbiome Species 0.000 description 6
- 238000009395 breeding Methods 0.000 description 5
- 230000001488 breeding effect Effects 0.000 description 5
- 238000005469 granulation Methods 0.000 description 5
- 230000003179 granulation Effects 0.000 description 5
- 150000002500 ions Chemical class 0.000 description 5
- QDHHCQZDFGDHMP-UHFFFAOYSA-N Chloramine Chemical compound ClN QDHHCQZDFGDHMP-UHFFFAOYSA-N 0.000 description 4
- IOVCWXUNBOPUCH-UHFFFAOYSA-M Nitrite anion Chemical compound [O-]N=O IOVCWXUNBOPUCH-UHFFFAOYSA-M 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- 241000894006 Bacteria Species 0.000 description 3
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 3
- 230000000052 comparative effect Effects 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 238000005342 ion exchange Methods 0.000 description 3
- 229910052757 nitrogen Inorganic materials 0.000 description 3
- NLKNQRATVPKPDG-UHFFFAOYSA-M potassium iodide Chemical compound [K+].[I-] NLKNQRATVPKPDG-UHFFFAOYSA-M 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- 239000008399 tap water Substances 0.000 description 3
- 235000020679 tap water Nutrition 0.000 description 3
- 241000252229 Carassius auratus Species 0.000 description 2
- 241000238557 Decapoda Species 0.000 description 2
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 2
- TWRXJAOTZQYOKJ-UHFFFAOYSA-L Magnesium chloride Chemical compound [Mg+2].[Cl-].[Cl-] TWRXJAOTZQYOKJ-UHFFFAOYSA-L 0.000 description 2
- 241001465754 Metazoa Species 0.000 description 2
- JVMRPSJZNHXORP-UHFFFAOYSA-N ON=O.ON=O.ON=O.N Chemical compound ON=O.ON=O.ON=O.N JVMRPSJZNHXORP-UHFFFAOYSA-N 0.000 description 2
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 2
- 230000002411 adverse Effects 0.000 description 2
- 230000008859 change Effects 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- 238000004737 colorimetric analysis Methods 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 238000001125 extrusion Methods 0.000 description 2
- 235000013305 food Nutrition 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 238000000691 measurement method Methods 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 230000001546 nitrifying effect Effects 0.000 description 2
- 239000003002 pH adjusting agent Substances 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 230000000644 propagated effect Effects 0.000 description 2
- 230000029058 respiratory gaseous exchange Effects 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 description 2
- 231100000331 toxic Toxicity 0.000 description 2
- 230000002588 toxic effect Effects 0.000 description 2
- KZBUYRJDOAKODT-UHFFFAOYSA-N Chlorine Chemical compound ClCl KZBUYRJDOAKODT-UHFFFAOYSA-N 0.000 description 1
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 1
- 241000530454 Litopenaeus schmitti Species 0.000 description 1
- JLVVSXFLKOJNIY-UHFFFAOYSA-N Magnesium ion Chemical compound [Mg+2] JLVVSXFLKOJNIY-UHFFFAOYSA-N 0.000 description 1
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 1
- 229920002472 Starch Polymers 0.000 description 1
- MMDJDBSEMBIJBB-UHFFFAOYSA-N [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] Chemical compound [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] MMDJDBSEMBIJBB-UHFFFAOYSA-N 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- QVQLCTNNEUAWMS-UHFFFAOYSA-N barium oxide Inorganic materials [Ba]=O QVQLCTNNEUAWMS-UHFFFAOYSA-N 0.000 description 1
- 230000004071 biological effect Effects 0.000 description 1
- 238000010170 biological method Methods 0.000 description 1
- 235000008429 bread Nutrition 0.000 description 1
- 125000003178 carboxy group Chemical group [H]OC(*)=O 0.000 description 1
- 229920003123 carboxymethyl cellulose sodium Polymers 0.000 description 1
- 229940084030 carboxymethylcellulose calcium Drugs 0.000 description 1
- 229940063834 carboxymethylcellulose sodium Drugs 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 229910001882 dioxygen Inorganic materials 0.000 description 1
- 235000019441 ethanol Nutrition 0.000 description 1
- 230000029142 excretion Effects 0.000 description 1
- 238000011049 filling Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 229910052736 halogen Inorganic materials 0.000 description 1
- 150000002367 halogens Chemical class 0.000 description 1
- 150000004679 hydroxides Chemical class 0.000 description 1
- 229910001629 magnesium chloride Inorganic materials 0.000 description 1
- 229910001425 magnesium ion Inorganic materials 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229960002900 methylcellulose Drugs 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 239000004745 nonwoven fabric Substances 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 230000020477 pH reduction Effects 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 239000011164 primary particle Substances 0.000 description 1
- 230000000384 rearing effect Effects 0.000 description 1
- 238000005096 rolling process Methods 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 235000014102 seafood Nutrition 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 239000001488 sodium phosphate Substances 0.000 description 1
- 229910000162 sodium phosphate Inorganic materials 0.000 description 1
- 241000894007 species Species 0.000 description 1
- 229940032147 starch Drugs 0.000 description 1
- 239000008107 starch Substances 0.000 description 1
- 235000019698 starch Nutrition 0.000 description 1
- IATRAKWUXMZMIY-UHFFFAOYSA-N strontium oxide Inorganic materials [O-2].[Sr+2] IATRAKWUXMZMIY-UHFFFAOYSA-N 0.000 description 1
- 230000004083 survival effect Effects 0.000 description 1
- 230000035899 viability Effects 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Landscapes
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Water Treatment By Sorption (AREA)
Abstract
Description
本発明は、水質浄化、特に水中に溶存するアンモニア及び亜硝酸の除去に関し、海、川、池、沼等の水域や、観賞魚用水槽、いけす用水槽、活魚・観賞魚輸送用のプラスチック製袋等の閉鎖性水域及び水道水、工業用水、下水その他の水の利用における水質低下防止に関する。
さらに詳しくは、周期表第2A族に属する元素からなる化合物を水中に浸漬させることによって、水中のアンモニア及び亜硝酸を簡便に除去することができる水質浄化剤を提供することである。
The present invention relates to water purification, particularly removal of ammonia and nitrous acid dissolved in water, water areas such as seas, rivers, ponds, swamps, ornamental fish tanks, fish tanks, live fish and ornamental fish The present invention relates to prevention of water quality deterioration in the use of closed water areas such as bags and tap water, industrial water, sewage and other water.
More specifically, it is to provide a water purification agent capable of easily removing ammonia and nitrous acid in water by immersing a compound comprising an element belonging to Group 2A of the periodic table in water.
一般に、水中に溶存するアンモニア及び亜硝酸は、水棲生物、その他の生体に悪影響を及ぼすおそれがあり、海、川、池、沼等の水域や、観賞魚用水槽、いけす用水槽、活魚・観賞魚輸送用のプラスチック製袋等の閉鎖性水域及び水道水、工業用水、下水その他の水に溶存するアンモニア及び亜硝酸が、種々の方法で処理されている。 In general, ammonia and nitrous acid dissolved in water may adversely affect aquatic organisms and other living organisms. Water such as seas, rivers, ponds, swamps, ornamental fish tanks, fish tanks, live fish and ornamentals Ammonia and nitrous acid dissolved in closed water areas such as plastic bags for transporting fish and tap water, industrial water, sewage and other water are treated in various ways.
例えば、水中のアンモニアを除去する方法としては、生物的処理、塩素添加による処理、イオン交換による処理、その他に特許文献1〜4に開示されている方法などがある。 For example, methods for removing ammonia in water include biological treatment, treatment by addition of chlorine, treatment by ion exchange, and other methods disclosed in Patent Documents 1 to 4.
生物的処理方法は、アンモニア及び亜硝酸を分解する微生物を付着、繁殖させた担体に処理水を接触させ、微生物による酸化を利用した処理方法であるが、装置の設置スペースがかなり大きくなることや微生物が定着するまでに時間がかかるというような問題がある。 The biological treatment method is a treatment method that utilizes oxidation by microorganisms by contacting treated water with a carrier on which microorganisms that decompose ammonia and nitrous acid are attached and propagated. There is a problem that it takes time for the microorganisms to settle.
イオン交換による処理方法は、イオン交換能を有する物質(イオン交換体)のイオンと水中のイオンとを交換することにより、アンモニウムイオンを除去する方法であるが、設置スペースやイオン交換体を再生処理する時に高濃度のアンモニウムイオン含有排水が排出されるという問題がある。 The treatment method by ion exchange is a method of removing ammonium ions by exchanging ions of a substance having ion exchange ability (ion exchanger) and ions in water, but the installation space and the ion exchanger are regenerated. There is a problem that wastewater containing ammonium ions with a high concentration is discharged.
塩素処理法は、処理水に塩素ガスを注入し、水中のアンモニアと塩素とを反応させクロラミン(結合塩素)を生じさせる。塩素の注入量の増加に伴ってクロラミンの量は増加してやがて極大点に達し、次いで、クロラミンは更に加えられた過剰の塩素によって分解され窒素を生じクロラミンは分解されて無くなり、アンモニアは除去される。しかし、アンモニアを完全に除去するために、実際の処理ではやや過剰の塩素を加えるため、水中に遊離残留塩素が残ってしまい、水棲生物、その他の生体に悪影響を及ぼすおそれがあり、残留塩素を除去しなければならないという問題がある。 In the chlorine treatment method, chlorine gas is injected into treated water, and ammonia and chlorine in the water are reacted to produce chloramine (bound chlorine). As the amount of chlorine injected increases, the amount of chloramine increases and eventually reaches a maximum point, and then chloramine is further decomposed by excess chlorine added to form nitrogen, chloramine is decomposed and eliminated, and ammonia is removed. The However, in order to completely remove ammonia, a slight excess of chlorine is added in the actual treatment, leaving free residual chlorine in the water, which may adversely affect aquatic organisms and other living organisms. There is a problem that must be removed.
また、特許文献1には、アンモニア性窒素が溶存している水に酸化剤を注入して水中のアンモニアを分解し、発生した気体を脱気装置で除去する方法が開示されているが、やはりアンモニアを除去する装置の設置スペースが大きくなるなどの問題がある。 Patent Document 1 discloses a method of injecting an oxidizing agent into water in which ammoniacal nitrogen is dissolved to decompose ammonia in the water and removing the generated gas with a deaeration device. There is a problem that the installation space of the apparatus for removing ammonia becomes large.
特許文献2には、水中のアンモニアを除去するための酸化チタン成形体が開示されているが、この際、酸化チタン成形体に紫外線を照射する必要があり、紫外線ランプを特別に設置しなければならないなどの問題がある。 Patent Document 2 discloses a titanium oxide molded body for removing ammonia in water. At this time, it is necessary to irradiate the titanium oxide molded body with ultraviolet rays, and unless an ultraviolet lamp is specially installed. There are problems such as not becoming.
特許文献3には、底部に散気装置を配置した水処理方法が開示されており、処理槽に保持された硝化菌によって処理水中のアンモニア成分が硝化されることが記載されているが、アンモニアを除去する装置の設置スペースが大きくなることや硝化菌を定着させるまでに時間がかかるなどの問題がある。 Patent Document 3 discloses a water treatment method in which an air diffuser is arranged at the bottom, and it is described that ammonia components in treated water are nitrified by nitrifying bacteria held in a treatment tank. There is a problem that the installation space of the apparatus for removing the odor increases, and it takes time until the nitrifying bacteria are fixed.
特許文献4には、アンモニア性窒素を含む水にハロゲンを添加し、さらにオゾンで処理し、水中のアンモニア性窒素を分解する方法が開示されている。生物濾過槽のような大掛かりな装置は必要ではないが、薬剤を添加し、pHをコントロールする工程が必要であり操作が繁雑であるなどの問題がある。 Patent Document 4 discloses a method of decomposing ammonia nitrogen in water by adding halogen to water containing ammonia nitrogen and further treating with ozone. Although a large-scale apparatus such as a biological filtration tank is not necessary, there is a problem that a process of adding a chemical and controlling pH is necessary and the operation is complicated.
いずれの場合も、設備が大掛かりであったり、処理工程が長くなったり、高濃度のアンモニアの処理には適していても、水量が少なくかつ低濃度のアンモニア処理においては費用対効果が適当でなかったり、設置スペースの問題や、アンモニアの処理操作が煩雑であるといった問題がある。 In either case, the equipment is large, the treatment process is long, and it is suitable for the treatment of high-concentration ammonia, but it is not cost-effective in the treatment of low-concentration ammonia with a small amount of water. In addition, there are problems such as installation space and complicated ammonia processing operations.
例えば、前記のような大掛かりな方法でアンモニア及び亜硝酸の処理ができない観賞魚用水槽、いけす用水槽、活魚・観賞魚輸送用のプラスチック製袋等で使用される飼育水は、魚等の水棲生物から排泄されるアンモニアにより水質が悪化したり、魚等の水棲生物の呼吸により水中の炭酸ガス濃度の上昇が著しく起こる。そして、魚等の水棲生物の活力低下やへい死が起こるという問題がある。 For example, breeding water used in aquariums for ornamental fish that cannot be treated with ammonia and nitrous acid by the large-scale method as described above, cistern tanks, plastic bags for transporting live fish and ornamental fish, etc. The water quality deteriorates due to ammonia excreted from the organism, and the concentration of carbon dioxide in the water increases significantly due to the respiration of aquatic organisms such as fish. And there is a problem that the vitality of aquatic organisms such as fish is reduced and death occurs.
少量の飼育水中で魚等の水棲生物を飼うと、排泄物、残り餌、水草の枯れたものなどがアンモニア性窒素の原因となり、さらに排泄物の中にいる亜硝酸菌の分解作用で亜硝酸性窒素となり、これが魚等の水棲生物に有害になる。 When aquatic organisms such as fish are kept in a small amount of breeding water, excrement, residual food, and withered aquatic plants cause ammonia nitrogen, and nitrite is decomposed by nitrite bacteria in the excrement. Nitrogen, which is harmful to aquatic organisms such as fish.
亜硝酸(NO3)は、アンモニアが酸化分解されたもので水棲生物、その他の生体に対して有毒で、水槽等の飼育水の初期や過密飼育、大量に給餌した場合などに特に発生しやすい。 Nitrous acid (NO 3 ) is oxidatively decomposed ammonia, and is toxic to aquatic organisms and other living organisms. It is particularly likely to occur in the early and overcrowded breeding water of aquariums, etc. .
毒性のある亜硝酸性窒素を速やかに分解するためには、微生物をうまく繁殖させ、比較的安定した害の少ない硝酸性窒素に変化させ水質を浄化させる方法などがとられるが、この方法は微生物が定着し効果を発揮するまで数週間ぐらいかかるという問題がある。 In order to quickly decompose toxic nitrite nitrogen, microorganisms can be propagated well, and the water quality can be purified by changing to relatively stable and less harmful nitrate nitrogen. There is a problem that it takes several weeks for the to settle and to exert the effect.
水量の多い水系では、このような急激な水質の悪化は、起こりにくい。これに対し、前記の活魚・観賞魚輸送用のプラスチック製袋等での水輸送では、水量が極端に少なく、水温、pHなどの変化により、急激に有害な亜硝酸性窒素が発生し、その濃度が高くなると、魚が死に至る場合がある。死に至らない場合でも魚は、ストレスを感じ病気になり易くなる等害が生じる。 In a water system having a large amount of water, such a rapid deterioration of water quality is unlikely to occur. On the other hand, in the water transport using the plastic bag for transporting the live fish and ornamental fish, the amount of water is extremely small, and harmful nitrite nitrogen is rapidly generated due to changes in the water temperature, pH, etc. High concentrations can cause fish to die. Even if it does not lead to death, the fish suffers damage such as being stressed and prone to illness.
プラスチック製袋輸送は、プラスチック製袋に水と魚等の水棲生物を入れ、ヘッドスペースのある状態にして密封し、さらに段ボール箱などに入れて輸送する方法で、小規模、短時間の輸送に用いられる。プラスチック製袋輸送は、低コストで簡便な方法であり、養殖魚、天然魚、或いは観賞魚の輸送に広く用いられている。 Plastic bag transport is a method of transporting water and fish and other aquatic organisms in a plastic bag, sealing it with a headspace, and then transporting it in a cardboard box. Used. Plastic bag transportation is a low-cost and simple method, and is widely used for transportation of cultured fish, natural fish, or ornamental fish.
しかし、プラスチック製袋輸送では、輸送中の水温、溶存酸素濃度、水質をコントロールすることができないため、短時間の輸送でも、輸送中の魚の活力低下やへい死が発生しやすいという問題がある。
そのためプラスチック製袋輸送では、輸送中の魚等の水棲生物の活力低下やへい死を防ぐため、密封する水の温度を下げたり、ヘッドスペース部に酸素ガスを封入したり、餌止めするといったさまざまな工夫が施されている。
However, in plastic bag transportation, since the water temperature, dissolved oxygen concentration, and water quality during transportation cannot be controlled, there is a problem in that the vitality of fish during transportation and mortality are likely to occur even during short transportation.
Therefore, in plastic bag transport, various measures such as lowering the temperature of the water to be sealed, enclosing oxygen gas in the headspace, and stopping food to prevent the loss of vitality and death of aquatic organisms such as fish during transport. Ingenuity is given.
しかし、これらの方法だけでは、魚等の水棲生物の活力低下やへい死を防ぐのに十分でなく、特に気温が上昇する夏場では、活力が低下したり、死滅し、魚等の水棲生物の商品価値が著しく低下してしまう。 However, these methods alone are not sufficient to prevent the decline of vitality and death of aquatic organisms such as fish. Especially in the summer when the temperature rises, the vitality of the aquatic organisms declines or disappears, and products of aquatic organisms such as fish. The value is significantly reduced.
観賞魚では特に重大な問題で、輸送中にへい死した観賞魚は全く価値がなくなってしまい、活力のない場合や輸送袋中の一匹がへい死した場合でも著しく商品価値が低下する。 An aquarium fish is a particularly serious problem, and an aquarium fish that has died during transportation loses its value at all, and even if it is not vigorous or one animal in the transport bag dies, the merchandise value is significantly reduced.
観賞用の熱帯魚等の多くは、諸外国から航空機により輸送されている。また、国内の鑑賞用の金魚や錦鯉も生産地から各地域へトラック輸送されている。これらの観賞魚等の水輸送が他の水系と大きく異なる点は、短時間で少量の水を使用して運ばなければならないことである。 Many ornamental tropical fish are transported by air from other countries. Domestic goldfish and Nishikigoi are also trucked from the production area to each region. The major difference in water transportation of these ornamental fish from other water systems is that they must be transported using a small amount of water in a short time.
輸送水量が少ない観賞魚等の場合は、他の水系のような水質を浄化する大掛かりな装置を導入したり、薬剤を添加した煩雑な操作は、経済的にみて輸送コストの増大につながるため実施できない。 In the case of ornamental fish, etc. with a small amount of water to be transported, implementation of large-scale equipment for purifying water quality, such as other water systems, or complicated operations with chemicals added will lead to increased transportation costs from an economic perspective. Can not.
水量が少ないほど魚等の水棲生物の排泄物などが原因となり水質が悪くなるのが早くなり、水質の管理が非常に難しく、輸送できる魚の数が制限されてしまう。 The smaller the amount of water, the faster the water quality becomes worse due to the excrement of aquatic organisms such as fish, the water quality is very difficult to control, and the number of fish that can be transported is limited.
生物的な方法でアンモニア及び亜硝酸を処理するためには、微生物を定着させる必要があるが、新しい水をセットし、短時間の輸送において微生物は十分に定着しないため、この方法は適用できない。 In order to treat ammonia and nitrous acid by a biological method, it is necessary to fix microorganisms. However, this method cannot be applied because microorganisms are not sufficiently fixed by setting fresh water and transporting in a short time.
水処理設備の設置スペースが、十分にとれる場合は、アンモニア及び亜硝酸を除去し、水質浄化することもできるが、設置スペースが取れないなど物理的理由で、大掛かりな装置を導入できない場合は、アンモニア及び亜硝酸を除去することができない。
このため、輸送中の水温やpHの変化、排泄されるアンモニアにより魚等の水棲生物の活力が低下したり、へい死するのを防ぐ簡便な方法が望まれている。
If the installation space of the water treatment facility is sufficient, ammonia and nitrous acid can be removed and the water quality can be purified.However, if a large-scale device cannot be introduced due to physical reasons such as the installation space is not available, Ammonia and nitrous acid cannot be removed.
For this reason, there is a demand for a simple method for preventing the vitality of aquatic organisms such as fish from being lowered or dead due to changes in water temperature and pH during transportation and excreted ammonia.
本発明の課題は、特殊で大掛かりな装置や機器を用いずに、簡便な操作で安全で効果的に、水中のアンモニア及び亜硝酸を除去できる水質浄化剤を提供することである。 An object of the present invention is to provide a water purification agent capable of removing ammonia and nitrous acid in water safely and effectively by a simple operation without using a special and large-scale apparatus or equipment.
本発明者らは、前記課題を解決すべく種々検討を重ねた結果、海、川、池、沼等の水域や、観賞魚用水槽、いけす用水槽、活魚・観賞魚輸送用のプラスチック製袋等の閉鎖性水域及び水道水、工業用水、下水その他の水の利用において水質低下を防止するために、周期表第2A族に属する元素の化合物からなる水質浄化剤を水中に浸漬することによって、水中に溶存するアンモニア及び亜硝酸を効率よく除去することを見出し、特殊で大掛かりな装置や機器を用いずに、水質低下防止に効果がある最適な水質浄化剤を見出して、本発明に至ったものである。 As a result of various studies to solve the above-mentioned problems, the present inventors have found that water areas such as the sea, rivers, ponds and swamps, aquariums for aquarium fish, aquariums for fish, and plastic bags for transporting live fish and aquarium fish In order to prevent water quality degradation in the use of closed water areas such as tap water, industrial water, sewage and other water, etc., by immersing a water purification agent comprising a compound of an element belonging to Group 2A of the periodic table in water, The present inventors have found that ammonia and nitrous acid dissolved in water can be efficiently removed, and have found an optimal water purification agent that is effective in preventing deterioration of water quality without using special and large-scale equipment and equipment, and have reached the present invention. Is.
すなわち本発明は、周期表第2A族に属する元素の化合物からなり、アンモニア及び亜硝酸を除去する水質浄化剤に関する。ここで、前記化合物は、水酸化物または酸化物であることが好ましく、さらに酸化物は、酸化マグネシウム、酸化カルシウム、また水酸化物は、水酸化マグネシウム、水酸化カルシウムであることが好ましい。最も好ましくは、水酸化マグネシウムである。 That is, this invention relates to the water purification agent which consists of a compound of the element which belongs to periodic table 2A group, and removes ammonia and nitrous acid. Here, the compound is preferably a hydroxide or an oxide. Further, the oxide is preferably magnesium oxide or calcium oxide, and the hydroxide is preferably magnesium hydroxide or calcium hydroxide. Most preferred is magnesium hydroxide.
前記化合物は、粉末状、又は粉末をバインダで結着してなる造粒体或いは成形体として提供できる。 The compound can be provided in the form of a powder or a granulated body or a molded body formed by binding powder with a binder.
また、前記造粒体或いは成形体は、前記粉末に対して3〜30質量%のバインダを混合することが好ましく、更に好ましくは、5〜20質量%のバインダを混合して製造される。 Moreover, it is preferable that the said granulated body or molded object mixes 3-30 mass% binder with respect to the said powder, More preferably, 5-20 mass% binder is mixed and manufactured.
前記バインダは、非水溶性のもので、エチルセルロースその他のセルロース誘導体、メタクリル系共重合体、コロイダルシリカ、或いは、水溶性で溶解速度の遅いもので、デンプングリコール酸ナトリウム、デンプンリン酸エステルナトリウム、カルボキシメチルセルロースカルシウム、カルボキシメチルセルロースナトリウム、メチルセルロース、ヒドロキシポロピルメチルセルロース、ヒドロキシエチルメチルセルロース、ヒドロキシポロピルセルロース、アルギン酸ナトリウム、アルギン酸プロピレングリコールエステル、ポリアクリル酸ナトリウム、ポリビニルアルコール、ケイ酸ソーダからなる群から選ばれた1種或いは2種以上で製造することができる。 The binder is water-insoluble, such as ethyl cellulose or other cellulose derivative, methacrylic copolymer, colloidal silica, or water-soluble and slow dissolving rate, such as sodium starch glycolate, starch sodium phosphate ester, carboxy 1 selected from the group consisting of methylcellulose calcium, sodium carboxymethylcellulose, methylcellulose, hydroxypropylmethylcellulose, hydroxyethylmethylcellulose, hydroxypropylcellulose, sodium alginate, propylene glycol alginate, sodium polyacrylate, polyvinyl alcohol, sodium silicate It can be produced with two or more species.
前記造粒体或いは成形体は、直径が0.1〜10mmの大きさが好ましい。
また、処理水1リットルに対し、本発明の水質浄化剤を0.1〜20gを浸漬させ、水中のアンモニア、亜硝酸及び炭酸ガスを除去することができる。
The granulated body or molded body preferably has a diameter of 0.1 to 10 mm.
In addition, 0.1 to 20 g of the water purification agent of the present invention can be immersed in 1 liter of treated water to remove ammonia, nitrous acid, and carbon dioxide in the water.
本発明の水質浄化剤を用いることにより、高価で大掛かりな水質浄化設備や機器を用いることなく、少量の添加量で安価に、魚等の水棲生物の生活動による水質の劣化を抑止することができる。
特に、活魚・観賞魚等の輸送時や飼育時におけるアンモニア及び亜硝酸による水質悪化を防止し、環境変化による水棲生物のストレスを低下させ、生存率を高めることができる。また、輸送時間の延長が図れるため、これまで不可能であった遠方地域への活魚・観賞魚等のプラスチック製袋輸送が可能となる。さらに、輸送袋内に封入可能な魚介類の量を増やすことができるため、輸送費用のコストダウンができる。
By using the water purification agent of the present invention, it is possible to suppress the deterioration of water quality due to the biological activity of aquatic organisms such as fish, inexpensively with a small amount of addition, without using expensive and large-scale water purification facilities and equipment. it can.
In particular, it is possible to prevent deterioration of water quality due to ammonia and nitrous acid during transportation and rearing of live fish, ornamental fish, etc., reduce stress of aquatic organisms due to environmental changes, and increase survival rate. In addition, since the transportation time can be extended, it is possible to transport plastic bags of live fish, ornamental fish, etc. to distant areas, which was impossible until now. Furthermore, since the amount of seafood that can be enclosed in the transport bag can be increased, the cost of transport can be reduced.
本発明は、従来、一般に使用されていた、高価で大掛かりな水質浄化設備や機器、薬剤等を用いた煩雑な操作を用いることなく、簡便に水中のアンモニア及び亜硝酸を処理できる水質浄化剤を提供する。 The present invention provides a water purification agent that can easily treat ammonia and nitrous acid in water without using complicated and expensive operations such as expensive and large-scale water purification equipment, equipment, chemicals, etc. that have been generally used. provide.
本発明の水質浄化剤を水中に浸漬させることにより、魚等の水棲生物の排泄や呼吸により輸送用プラスチック製袋等に生じたアンモニア、亜硝酸や炭酸ガスを効率的に除去することができ、魚等の水棲生物の活力低下やへい死を防止することができる。 By immersing the water purification agent of the present invention in water, it is possible to efficiently remove ammonia, nitrous acid and carbon dioxide generated in plastic bags for transportation due to excretion and respiration of aquatic organisms such as fish, It can prevent a decrease in vitality and death of aquatic organisms such as fish.
前記の水質浄化剤は、周期表第2A族に属する元素の化合物からなり、好ましくは、それらの水酸化物または酸化物からなる化合物である。更に好ましくは、酸化マグネシウム、酸化カルシウム、水酸化マグネシウム、水酸化カルシウムを原料に用いることである。 The water purification agent is composed of a compound of an element belonging to Group 2A of the periodic table, preferably a compound composed of a hydroxide or an oxide thereof. More preferably, magnesium oxide, calcium oxide, magnesium hydroxide, or calcium hydroxide is used as a raw material.
周期率表第2A族に属する元素の酸化物は、MgO、CaO、SrO、BaOの順に水との反応性は激しくなる。それに対して水酸化物は、水との反応は緩やかであるがその酸化物に比べ分子量が大きく、同重量添加した場合では、効果は異なる。これらの点を考慮して、水中のアンモニア及び亜硝酸を効率よく除去する水質浄化剤としては、酸化マグネシウム、酸化カルシウム、水酸化マグネシウム、水酸化カルシウムが適していることを見出した。更に、水へ浸漬して使用する材料として、安全性も考慮すると水酸化マグネシウムが最も好ましい。 The oxides of elements belonging to Group 2A of the periodic table become more reactive with water in the order of MgO, CaO, SrO, BaO. In contrast, hydroxides have a slow reaction with water, but have a higher molecular weight than that of the oxides. In view of these points, it has been found that magnesium oxide, calcium oxide, magnesium hydroxide, and calcium hydroxide are suitable as water purification agents that efficiently remove ammonia and nitrous acid in water. Furthermore, magnesium hydroxide is most preferable as a material to be used by immersing in water in consideration of safety.
本発明の水質浄化剤の原料となる水酸化マグネシウム等は、魚等の水棲生物に有害なイオンが溶出する恐れがないものが良く、純度は、90質量%以上であることが好ましい。更に好ましくは95質量%以上である。 Magnesium hydroxide or the like used as a raw material for the water purification agent of the present invention is good in that there is no fear of eluting ions harmful to aquatic organisms such as fish, and the purity is preferably 90% by mass or more. More preferably, it is 95 mass% or more.
前記水酸化マグネシウムは、塩化マグネシウム溶液等のマグネシウムイオン含有溶液とアルカリ沈殿剤とを攪拌させながら混合し、所定時間反応させて1次粒子を生成させ、ろ過、洗浄し、乾燥することにより製造することができる。
原料として使用する水酸化マグネシウムは、前記のような公知の方法で合成してもよいし、一般に市販されている水酸化マグネシウムを使用してもよい。
The magnesium hydroxide is produced by mixing a magnesium ion-containing solution such as a magnesium chloride solution and an alkali precipitant while stirring and reacting for a predetermined time to produce primary particles, which are filtered, washed and dried. be able to.
Magnesium hydroxide used as a raw material may be synthesized by a known method as described above, or commercially available magnesium hydroxide may be used.
また、本発明の水質浄化剤は、粉末状のまま、或いはバインダで結着して造粒体や成形体を水に浸漬させてもよいし、取扱い易さからそれらを容器や不織布に充填して使用することもできる。 In addition, the water purification agent of the present invention may be powdered or bound with a binder to immerse the granulated body or molded body in water, or fill them into a container or nonwoven fabric for ease of handling. Can also be used.
造粒や成形方法としては、押し出し成形、マルメライザー法、パン造粒、転動造粒、押出造粒、攪拌造粒、一軸プレス成形、CIP成形等公知で任意の方法を採用することができる。 As the granulation and molding method, any known method such as extrusion molding, Malmerizer method, bread granulation, rolling granulation, extrusion granulation, stirring granulation, uniaxial press molding, CIP molding, etc. can be adopted. .
使用するバインダとしては、水に対し安定な非水溶性のものを使用でき、代表的なものとしては、エチルセルロースその他のセルロース誘導体、メタクリル系共重合体、コロイダルシリカなどが挙げられる。 As the binder to be used, water-insoluble and water-insoluble ones can be used, and typical examples include ethyl cellulose and other cellulose derivatives, methacrylic copolymers, colloidal silica, and the like.
また、水溶性で溶解速度の遅いバインダも使用することができ、デンプングリコール酸ナトリウム、デンプンリン酸エステルナトリウム、カルボキシメチルセルロースカルシウム、カルボキシメチルセルロースナトリウム、メチルセルロース、ヒドロキシポロピルメチルセルロース、ヒドロキシエチルメチルセルロース、ヒドロキシポロピルセルロース、アルギン酸ナトリウム、アルギン酸プロピレングリコールエステル、ポリアクリル酸ナトリウム、ポリビニルアルコール、ケイ酸ソーダが代表的なものとして挙げられるが、これらに限定されるものではない。これらのバインダは、単独或いは2種以上を組み合わせて使用することができる。 A water-soluble binder with a low dissolution rate can also be used, such as sodium starch glycolate, sodium starch phosphate ester, carboxymethylcellulose calcium, carboxymethylcellulose sodium, methylcellulose, hydroxypropylmethylcellulose, hydroxyethylmethylcellulose, hydroxypropyl. Typical examples include, but are not limited to, cellulose, sodium alginate, propylene glycol alginate, sodium polyacrylate, polyvinyl alcohol, and sodium silicate. These binders can be used alone or in combination of two or more.
前記から選ばれた少なくとも1種以上のバインダを使用して、本発明の水質浄化剤が製造できる。前記造粒体或いは成形体は、0.1〜10mmの大きさが好ましく、処理水1リットルに対して0.1〜20gを浸漬させて使用することが好ましい。 The water purification agent of the present invention can be produced using at least one binder selected from the above. The granulated body or molded body preferably has a size of 0.1 to 10 mm, and is preferably used by immersing 0.1 to 20 g in 1 liter of treated water.
本発明の水質浄化剤は、水中に浸漬させて、水中のアンモニア及び亜硝酸を効率よく除去することができる。さらに、炭酸ガスの除去やpH調整剤としても作用する。通常、魚等の水棲生物の生活動により、水質は低pHになるが、本発明の水質浄化剤を浸漬させると中和反応によりpH低下を抑止することができる。 The water purification agent of the present invention can be immersed in water to efficiently remove ammonia and nitrous acid in water. Further, it acts as a carbon dioxide removal and pH adjuster. Usually, the water quality becomes low pH due to the life activity of aquatic organisms such as fish, but when the water purification agent of the present invention is immersed, the pH reduction can be suppressed by the neutralization reaction.
また、本発明の水質浄化剤は、単独で使用するほか、公知の炭酸ガス吸着剤やpH調整剤と混合して構成比率を変化させることにより、アンモニア、亜硝酸、炭酸ガス及びpH調整機能を任意に増減させることもでき、水量及び水質に応じて或いは魚等の水棲生物に対する安全性等の様々な環境条件から最適な配合状態を造ることが可能となる。 In addition to using the water purification agent of the present invention alone, it can be mixed with a known carbon dioxide adsorbent or pH adjuster to change the composition ratio, thereby providing ammonia, nitrous acid, carbon dioxide and pH adjusting functions. It can be arbitrarily increased or decreased, and it is possible to create an optimum blended state from various environmental conditions such as the safety against aquatic organisms such as fish according to the amount and quality of water.
本発明の水質浄化剤は、その表面に水中のアンモニア及び亜硝酸を吸着することができる。 The water purification agent of the present invention can adsorb ammonia and nitrous acid in water on its surface.
本発明の水質浄化剤は、粉末状、造粒体、成形体にしたものを水中に浸漬させて使用するに限らず、様々な容器に充填して使用することもでき、水循環装置のフィルター部に設置するなど循環水と接触させることでも効果を発揮させることができる。 The water purification agent of the present invention is not limited to use in the form of powder, granulated body, and molded body soaked in water, and can be used by filling various containers. The effect can also be exerted by bringing it into contact with circulating water, such as by installing it in the water.
本発明を実施例により具体的に説明するが、本発明は以下の実施例に限定されるものではない。 EXAMPLES The present invention will be specifically described with reference to examples, but the present invention is not limited to the following examples.
[実施例1]
水酸化マグネシウム粉末、純度99質量%(商品名:マグスター、タテホ化学工業(株)製)3000gにエチルセルロース10質量%をエチルアルコール1600mlに溶解した溶液を添加し、混練機(商品名:万能混合攪拌機、(株)ダルトン製)で混練し、乾燥機で80℃×24時間乾燥させた。次いで粉砕機で粉砕し、箱型篩いを通して3.6〜1.0mmの顆粒を得た。
[Example 1]
Magnesium hydroxide powder, purity 99% by mass (trade name: Magstar, manufactured by Tateho Chemical Co., Ltd.), a solution prepared by dissolving 10% by mass of ethyl cellulose in 1600 ml of ethyl alcohol was added to 3000 g, and kneader (trade name: universal mixing stirrer). , Manufactured by Dalton Co., Ltd.) and dried in a dryer at 80 ° C. for 24 hours. Subsequently, the mixture was pulverized by a pulverizer and passed through a box type sieve to obtain 3.6 to 1.0 mm granules.
[アンモニア濃度測定方法]
アンモニア濃度の測定は、ヨウ化第二水銀カリウム溶液(ネスラー試薬、関東化学)を用いて、褐色の錯塩を生成させ、比色法により定量した。
[Ammonia concentration measurement method]
Measurement of the ammonia concentration was carried out by using a mercuric potassium iodide solution (Nessler's reagent, Kanto Kagaku) to produce a brown complex salt and quantifying it by a colorimetric method.
[亜硝酸濃度測定方法]
亜硝酸濃度の測定は、市販のテトラテスト亜硝酸試薬(テトラジャパン(株))を用いて比色法により定量した。
[Nitrite concentration measurement method]
The concentration of nitrous acid was quantified by a colorimetric method using a commercially available tetratest nitrite reagent (Tetra Japan Co., Ltd.).
[試験水の調整]
50リットルの水槽に水を入れ、その中で中型の金魚(約150g/匹)12匹を飼育し、アンモニア濃度を上昇させた飼育水を準備し、この飼育水を水で3倍に希釈し、アンモニア濃度5ppmの試験水とした。
[Test water adjustment]
Pour water into a 50 liter tank, raise 12 medium-sized goldfish (about 150 g / animal), prepare breeding water with increased ammonia concentration, and dilute this breeding water 3 times with water. Test water having an ammonia concentration of 5 ppm was used.
実施例1の顆粒を予め調整したアンモニア濃度5ppmの試験水1リットルに、5g浸漬させ、室温で3日放置し、アンモニア濃度を測定した。
測定結果は、表1に示すとおりであり、水中のアンモニア濃度が減少していることがわかる。
5 g of the granule of Example 1 was immersed in 1 liter of preliminarily prepared test water having an ammonia concentration of 5 ppm and left at room temperature for 3 days to measure the ammonia concentration.
A measurement result is as showing in Table 1, and it turns out that the ammonia concentration in water is reducing.
[比較例1]
比較例として、予め調整したアンモニア濃度5ppmの試験水1リットルに本発明の水質浄化剤を浸漬させずに、室温で3日放置し、アンモニア濃度を測定した。測定結果は、表1のとおりであり、試験前も試験後も水中のアンモニア濃度が変化していないことがわかる。
[Comparative Example 1]
As a comparative example, the ammonia concentration was measured by leaving the water purifier of the present invention for 1 day at room temperature without immersing it in 1 liter of test water having an ammonia concentration of 5 ppm. The measurement results are as shown in Table 1. It can be seen that the ammonia concentration in the water did not change before and after the test.
[実施例2]
300mlのビーカーに250mlの水とシラサエビ15尾を入れ、そこに実施例1で作製した顆粒を3g浸漬させ、数日間室温で放置し、アンモニア濃度と亜硝酸濃度及び炭酸ガス濃度を測定した。アンモニア濃度の測定結果を表2、亜硝酸濃度の測定結果を表3に示す。
[Example 2]
In a 300 ml beaker, 250 ml of water and 15 tails of shrimp were placed, and 3 g of the granules produced in Example 1 were immersed therein and allowed to stand at room temperature for several days to measure ammonia concentration, nitrous acid concentration and carbon dioxide concentration. Table 2 shows the measurement results of the ammonia concentration, and Table 3 shows the measurement results of the nitrous acid concentration.
[比較例2]
300mlのビーカーに250mlの水とシラサエビ15尾を入れ、本発明品の水質浄化剤を浸漬させずに、数日間室温で放置し、アンモニア濃度と亜硝酸濃度及び炭酸ガス濃度を測定した。アンモニア濃度の測定結果を表2、亜硝酸濃度の測定結果を表3に示す。
[Comparative Example 2]
In a 300 ml beaker, 250 ml of water and 15 tails of shrimp were put and left at room temperature for several days without immersing the water purification agent of the present invention, and the ammonia concentration, nitrous acid concentration and carbon dioxide concentration were measured. Table 2 shows the measurement results of the ammonia concentration, and Table 3 shows the measurement results of the nitrous acid concentration.
表2、表3の結果から本発明の水質浄化剤を用いた実施例2は、アンモニア濃度及び亜硝酸濃度は低く維持された。その結果、シラサエビの生存率は高かった。また、本発明の処理剤を用いた実施例2は、炭酸ガス濃度も低く維持された。 From the results of Tables 2 and 3, in Example 2 using the water purification agent of the present invention, the ammonia concentration and the nitrous acid concentration were kept low. As a result, viability of white shrimp was high. In Example 2 using the treatment agent of the present invention, the carbon dioxide gas concentration was also kept low.
以上の結果から明らかなように、本発明の水質浄化剤は、魚等の水棲生物に有害となる水中に溶存しているアンモニア及び亜硝酸を除去することができる。また、本発明の水質浄化剤を使用した水中のアンモニア及び亜硝酸の除去方法は簡便であり、大掛かりな設備や煩雑な処理工程を必要とせず、低コストで行うことができる。
As is clear from the above results, the water purification agent of the present invention can remove ammonia and nitrous acid dissolved in water that are harmful to aquatic organisms such as fish. Moreover, the removal method of ammonia and nitrous acid in water using the water purification agent of the present invention is simple, can be performed at low cost without requiring large-scale equipment and complicated processing steps.
Claims (9)
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Cited By (5)
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CN103265101A (en) * | 2013-05-10 | 2013-08-28 | 中国科学院合肥物质科学研究院 | Forming flocculating agent capable of controlling dissolving rate according to water flow speed |
KR101762551B1 (en) * | 2016-11-07 | 2017-08-04 | 서정율 | Process for producing granular water treatment agent |
CN107804903A (en) * | 2017-11-15 | 2018-03-16 | 新沂市晶润石英材料有限公司 | A kind of technique for preparing composite flocculation agent using quartz sand dust |
WO2020255957A1 (en) * | 2019-06-20 | 2020-12-24 | 株式会社杉田製線 | Water purification material and water purification method using same |
CN114364639A (en) * | 2019-06-20 | 2022-04-15 | 株式会社杉田制线 | Water purification material having iron as main component and method for manufacturing the same |
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Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
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CN103265101A (en) * | 2013-05-10 | 2013-08-28 | 中国科学院合肥物质科学研究院 | Forming flocculating agent capable of controlling dissolving rate according to water flow speed |
CN103265101B (en) * | 2013-05-10 | 2014-08-27 | 中国科学院合肥物质科学研究院 | Forming flocculating agent capable of controlling dissolving rate according to water flow speed |
KR101762551B1 (en) * | 2016-11-07 | 2017-08-04 | 서정율 | Process for producing granular water treatment agent |
CN107804903A (en) * | 2017-11-15 | 2018-03-16 | 新沂市晶润石英材料有限公司 | A kind of technique for preparing composite flocculation agent using quartz sand dust |
CN107804903B (en) * | 2017-11-15 | 2020-11-06 | 新沂市晶润石英材料有限公司 | Process for preparing composite flocculant by using quartz sand dust |
WO2020255957A1 (en) * | 2019-06-20 | 2020-12-24 | 株式会社杉田製線 | Water purification material and water purification method using same |
JP2021000585A (en) * | 2019-06-20 | 2021-01-07 | 株式会社杉田製線 | Water purification material and water purification method using the same |
CN114340783A (en) * | 2019-06-20 | 2022-04-12 | 株式会社杉田制线 | Water purification material and water purification method using the same |
CN114364639A (en) * | 2019-06-20 | 2022-04-15 | 株式会社杉田制线 | Water purification material having iron as main component and method for manufacturing the same |
JP7154598B2 (en) | 2019-06-20 | 2022-10-18 | 株式会社杉田製線 | Water purification material and water purification method using the same |
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