JPH04118098A - Water purifier - Google Patents
Water purifierInfo
- Publication number
- JPH04118098A JPH04118098A JP2238402A JP23840290A JPH04118098A JP H04118098 A JPH04118098 A JP H04118098A JP 2238402 A JP2238402 A JP 2238402A JP 23840290 A JP23840290 A JP 23840290A JP H04118098 A JPH04118098 A JP H04118098A
- Authority
- JP
- Japan
- Prior art keywords
- water
- aquarium
- bacteria
- tank
- fixed bed
- 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.)
- Pending
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 100
- 241000894006 Bacteria Species 0.000 claims abstract description 29
- 238000000746 purification Methods 0.000 claims description 31
- 238000009395 breeding Methods 0.000 claims description 15
- 230000001488 breeding effect Effects 0.000 claims description 15
- 229910052500 inorganic mineral Inorganic materials 0.000 claims description 11
- 239000011707 mineral Substances 0.000 claims description 11
- 239000000463 material Substances 0.000 claims description 8
- 230000001580 bacterial effect Effects 0.000 claims description 7
- 238000005192 partition Methods 0.000 claims description 4
- 230000000644 propagated effect Effects 0.000 claims description 2
- 238000000638 solvent extraction Methods 0.000 claims 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 abstract description 44
- 241000251468 Actinopterygii Species 0.000 abstract description 25
- 229910021529 ammonia Inorganic materials 0.000 abstract description 22
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 22
- 239000001301 oxygen Substances 0.000 abstract description 22
- 229910052760 oxygen Inorganic materials 0.000 abstract description 22
- 150000002823 nitrates Chemical class 0.000 abstract description 11
- 230000001954 sterilising effect Effects 0.000 abstract description 9
- 229910002651 NO3 Inorganic materials 0.000 abstract description 5
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 abstract description 5
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 abstract description 4
- 230000009471 action Effects 0.000 abstract description 4
- 230000002093 peripheral effect Effects 0.000 abstract description 4
- 238000010438 heat treatment Methods 0.000 abstract description 3
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 abstract description 2
- 239000001257 hydrogen Substances 0.000 abstract description 2
- 229910052739 hydrogen Inorganic materials 0.000 abstract description 2
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 2
- 244000053095 fungal pathogen Species 0.000 abstract 1
- 239000005416 organic matter Substances 0.000 description 15
- 241001148470 aerobic bacillus Species 0.000 description 8
- 238000004659 sterilization and disinfection Methods 0.000 description 8
- 244000052616 bacterial pathogen Species 0.000 description 5
- 230000000813 microbial effect Effects 0.000 description 5
- 244000005700 microbiome Species 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 241000209094 Oryza Species 0.000 description 4
- 235000007164 Oryza sativa Nutrition 0.000 description 4
- 238000000354 decomposition reaction Methods 0.000 description 4
- 235000009566 rice Nutrition 0.000 description 4
- 241001148471 unidentified anaerobic bacterium Species 0.000 description 4
- 230000000694 effects Effects 0.000 description 3
- 235000013305 food Nutrition 0.000 description 3
- 238000005469 granulation Methods 0.000 description 3
- 230000003179 granulation Effects 0.000 description 3
- 238000006864 oxidative decomposition reaction Methods 0.000 description 3
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 239000012190 activator Substances 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 239000000460 chlorine Substances 0.000 description 2
- 229910052801 chlorine Inorganic materials 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 210000003608 fece Anatomy 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 238000011144 upstream manufacturing Methods 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- IOVCWXUNBOPUCH-UHFFFAOYSA-M Nitrite anion Chemical compound [O-]N=O IOVCWXUNBOPUCH-UHFFFAOYSA-M 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- -1 ammonia Chemical class 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 238000012258 culturing Methods 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 238000002513 implantation Methods 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 238000003780 insertion Methods 0.000 description 1
- 230000037431 insertion Effects 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 230000002503 metabolic effect Effects 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- 229910017464 nitrogen compound Inorganic materials 0.000 description 1
- 150000002830 nitrogen compounds Chemical class 0.000 description 1
- 235000021110 pickles Nutrition 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 239000008213 purified water Substances 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 239000011435 rock Substances 0.000 description 1
- 229910052814 silicon oxide Inorganic materials 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 230000002747 voluntary effect Effects 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Farming Of Fish And Shellfish (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
Description
【発明の詳細な説明】
産業上の利用分野
本発明は、観賞魚用水槽の水や魚の養殖用水、風呂水な
どの水を浄化する家庭用もしくは業務用水浄化装置、ま
た生ごみを砕き水に混ぜて汚泥水を浄化する水浄化装置
などに関するものである。DETAILED DESCRIPTION OF THE INVENTION Field of Industrial Application The present invention relates to a household or commercial water purification device for purifying water such as ornamental fish tank water, fish culture water, bath water, etc. This relates to water purification equipment that purifies sludge water by mixing it.
従来の技術
従来この種の水浄化装置は、例えば、実開昭58195
697号公報に示されるように、第5図のような構造に
なっている。即ち、紫外線ランプ31を内部に具えた紫
外線照射槽32、微生物着床体を具えた第1微生物処理
槽33第2微生物処理槽34が直列に接続されている。2. Description of the Related Art Conventionally, this type of water purification device has been proposed, for example, in Utility Model Application No. 58195.
As shown in Japanese Patent No. 697, it has a structure as shown in FIG. That is, an ultraviolet irradiation tank 32 equipped with an ultraviolet lamp 31 therein, a first microorganism treatment tank 33 and a second microorganism treatment tank 34 each equipped with a microorganism implantation body are connected in series.
各種間は、魚類飼育水槽(図示せず)ないし前記処理水
槽からの被処理水を前記処理水槽に導入するための導入
口35.36.37と被処理水を次の処理水槽、ないし
前記魚類飼育水槽へ送出するための吐出口38.39.
40とはホーフで接続されている。また、各微生物処理
槽の油粕を増進させる手段が備えられていない。Each space has an inlet 35, 36, 37 for introducing treated water from a fish breeding tank (not shown) or the treated water tank into the treated water tank, and an inlet 35, 36, 37 for introducing the treated water from the fish breeding tank (not shown) or the treated water tank into the treated water tank, and a port 35, 36, 37 for introducing the treated water from the fish breeding tank (not shown) or the treated water tank into the treated water tank. Outlet port 38.39 for sending out to breeding tank.
It is connected to 40 by a hof. Furthermore, there is no means for increasing the oil scum in each microbial treatment tank.
発明が解決しようとする課題
一般に、観賞魚水槽においては、水槽中の水は魚の代謝
作用と食べ残しの餅の分解と排泄物なとが原因でアンモ
ニアや汚れの発生、病原菌の繁殖などの問題がある。Problems to be Solved by the Invention In general, in aquarium fish tanks, the water in the tank has problems such as the generation of ammonia and dirt and the growth of pathogenic bacteria due to the metabolic effects of the fish, the decomposition of leftover rice cakes, and excrement. There is.
さらに、アンモニアなどの窒素化合物が分解する過程で
発生する亜硝酸や硝酸も大きな課題があった。Furthermore, nitrite and nitric acid, which are generated during the decomposition process of nitrogen compounds such as ammonia, also pose a major problem.
これらの課題を一部解決使用としたものとして最近上記
従来例に示すように微生物を利用した浄化フィルターや
紫外線による殺菌手段が提案され始めている。In order to partially solve these problems, recently, purification filters using microorganisms and sterilization means using ultraviolet light have begun to be proposed, as shown in the above-mentioned conventional examples.
上記従来の単に微生物処理槽を直列接続に接続した構成
では、微生物処理槽内を好気性菌の最適繁殖状態に維持
することができないという課題を有していた。The above-mentioned conventional configuration in which microbial treatment tanks are simply connected in series has a problem in that the interior of the microbial treatment tank cannot be maintained in an optimal breeding state for aerobic bacteria.
また、魚類飼育水槽(図示せず)と前記微生物処理槽と
の循環回路に挿入される循環ポンプ、空気挿入手段、及
びその取り付は位置が明示されていない。Furthermore, the positions of the circulation pump, air insertion means, and their attachments, which are inserted into the circulation circuit between the fish breeding tank (not shown) and the microbial treatment tank, are not clearly indicated.
本発明では、好気性菌、婢気性菌等繁殖状態が変わる複
数の細菌を効果的に繁殖させ浄化性能をより高めること
と、魚類飼育水槽と処理水槽間との循環回路に循環ポン
プ、空気挿入手段を配設した強制循環口B構成とし、回
路中に挿入された循環ポンプ、空気供給手段等の機器が
魚類飼育水槽で発生する排泄物によって動作不能となる
問題を解消することを目的とする。In the present invention, it is possible to effectively breed a plurality of bacteria that change their breeding state, such as aerobic bacteria and aerobic bacteria, to further improve purification performance, and to insert a circulation pump and air into the circulation circuit between the fish breeding tank and the treatment tank. The purpose of this system is to use a forced circulation port B configuration in which a means is provided, and to solve the problem that devices such as a circulation pump and an air supply means inserted into the circuit become inoperable due to excrement generated in a fish tank. .
さらに、細菌の固定床に鉱物質を用い浄化処理装置の浄
化性能を高めることを目的とする。Furthermore, the purpose is to improve the purification performance of the purification treatment equipment by using minerals as a fixed bed for bacteria.
課題を解決するための手段
上記課題を解決するために本発明は、水槽の水を循環さ
せる水圧送手段と浄化ユニットとを配設した強制循環流
路、底部壁面に流出路を有すると共に、水槽の底部に細
菌固定床を有した飼育水槽とからなる水浄化装置構成と
している。Means for Solving the Problems In order to solve the above problems, the present invention provides a forced circulation channel in which a water pressure feeding means for circulating water in an aquarium and a purification unit are provided, an outflow channel on the bottom wall surface, and a water tank. The water purification system consists of a breeding aquarium with a fixed bed of bacteria at the bottom.
水槽底部の細菌固定床は、繁殖条件が相異なる細菌が同
時に繁殖できるように複数個に分割された構成としてい
る。The fixed bacteria bed at the bottom of the tank is divided into multiple parts so that bacteria with different breeding conditions can breed at the same time.
更に、細菌を繁殖させる固定床は、CaO,5i0z
、Alz Os 、MgO,FeOが主成分とするアル
カリ成分を多く含んだ鉱物質で構成されている。Furthermore, the fixed bed for breeding bacteria is CaO,5i0z
, AlzOs , MgO, and FeO as the main components, and is composed of minerals containing a large amount of alkaline components.
作用
本発明は、上記構成によって、まず、さかなの排泄物や
食べ残しの餅などの有機物は水槽底部の細菌固定床に捕
獲され徐々に水中に溶解される。Operation According to the present invention, organic substances such as fish excrement and uneaten rice cakes are first captured in the bacteria fixed bed at the bottom of the aquarium and gradually dissolved in the water.
捕獲された有機物の一部は水槽底部の細菌固定床に培養
された細菌によりアンモニアや硝酸塩に分解される0次
に、有機物が分解され発生したアンモニアや硝酸塩を含
んだ水槽水は、循環ポンプにより浄化ユニットに送られ
、そこで嫌気性細菌群培養された第1モジユルに流入し
、モジュルの中の鉱物質の表面に膜状に付着した人工的
に培養された嫌気性細菌群と細菌活性化物質により、硝
酸塩は分解される。この硝酸塩が分解除去され、アンモ
ニアを含んだ水槽水は酸素供給手段で吸引された酸素を
含んだ空気と共に、第2モジユルへ流入する。ここで水
槽水中に含まれるアンモニアはモジュルの中の鉱物質の
表面に膜状に付着した人工的に培養された好気性細菌群
と細菌活性化物質により、酸素の多い雰囲気で効率よく
硝酸塩に酸化分解され、水は浄化される。Some of the captured organic matter is decomposed into ammonia and nitrate by bacteria cultured in a fixed bacterial bed at the bottom of the aquarium.Next, the aquarium water containing ammonia and nitrate generated by the decomposition of organic matter is removed by a circulation pump. The artificially cultivated anaerobic bacteria and bacteria activation substance flow into the first module, where they are sent to the purification unit and cultured there, and adhere to the surface of the mineral material in the module in a film form. , nitrates are decomposed. The nitrates are decomposed and removed, and the ammonia-containing aquarium water flows into the second module together with the oxygen-containing air sucked in by the oxygen supply means. Here, the ammonia contained in the aquarium water is efficiently oxidized to nitrate in an oxygen-rich atmosphere by an artificially cultured aerobic bacteria group and bacteria activator that adheres to the surface of the mineral material in the module in the form of a film. It is decomposed and the water is purified.
また、水槽中で繁殖した魚の病原菌類は、第1モジユル
、第2モジユルから流出した後、紫外線細菌ユニットに
流入し紫外線により死滅する。In addition, pathogenic bacteria of fish that have grown in the aquarium flow out from the first module and the second module and then flow into the ultraviolet bacteria unit where they are killed by ultraviolet rays.
このような浄化、細菌作用により、水槽中の水は常に清
浄な状態に保たれる。Due to this purification and bacterial action, the water in the aquarium is always kept clean.
実施例
以下、本発明の一実施例を添付図面に基づいて説明する
。第1図は、本発明の水浄化装置を応用した観賞魚用水
槽の外観図、第2図は同観賞魚用水槽の構成原理図であ
る。第1図、第2図において1は水槽、2は水槽lの台
で内部に水浄化ユニット3が内蔵されている。水浄化ユ
ニット3は鉱物質から成る微生物固定床が封入、並列に
配設された第1モジユル4、第2モジユル5と、イジェ
クタ−作用により外部空気を流水中に導入する酸素供給
手段6、前記第1モジユル4.5の上流側に設けたヒー
タ7と紫外線ランプ8が取り付けられた加熱殺菌ユニッ
ト9、及び、循環ポンプl101t弁11を基本要素と
して構成されている。第1モジユル4、第2モジユル5
には細菌が培養されている。培養されている細菌は、各
モジュールの用途に応じ同種菌、異種菌とに選定するこ
とができる。循環ポンプ10の流入路12は電磁弁11
を介し、水槽lの底へ連通している。加熱殺菌ユニット
9には流出路13が取りつけられ、清浄化された水は前
記流出路13を通り水槽lへ送られる。14はエアセパ
レータで、酸素供給手段6で吸引され、モジュール内に
流れ込んだ微細化された気泡を分離するものである。
15は空気用tMi弁で空気導入管1G中に取り付けら
れている。 17は水槽1、水浄化ユニット2からの漏
水を検知する漏水センサである。EXAMPLE Hereinafter, an example of the present invention will be described based on the accompanying drawings. FIG. 1 is an external view of an aquarium fish tank to which the water purification device of the present invention is applied, and FIG. 2 is a diagram showing the principle of construction of the aquarium fish tank. In FIGS. 1 and 2, 1 is a water tank, and 2 is a stand for the water tank l, which has a water purification unit 3 built therein. The water purification unit 3 includes a first module 4 and a second module 5, each of which contains a fixed bed of microorganisms made of mineral substances and which are arranged in parallel, an oxygen supply means 6 that introduces external air into the flowing water by an ejector action, and The basic elements are a heating sterilization unit 9 equipped with a heater 7 and an ultraviolet lamp 8 provided upstream of the first module 4.5, and a circulation pump l101t valve 11. 1st module 4, 2nd module 5
bacteria are cultured. The bacteria being cultured can be selected as homologous or heterologous depending on the purpose of each module. The inflow path 12 of the circulation pump 10 is a solenoid valve 11
It communicates with the bottom of the aquarium l via. An outflow path 13 is attached to the heat sterilization unit 9, and purified water is sent to the water tank l through the outflow path 13. Reference numeral 14 denotes an air separator that separates fine air bubbles that have been sucked in by the oxygen supply means 6 and have flowed into the module.
Reference numeral 15 denotes an air tMi valve installed in the air introduction pipe 1G. 17 is a water leakage sensor that detects water leakage from the water tank 1 and the water purification unit 2.
18は制御回路を内蔵した制御ボックスである。水槽2
の底部には、細菌を培養するための固定床19が敷き詰
められている。18 is a control box containing a control circuit. Aquarium 2
A fixed bed 19 for culturing bacteria is placed at the bottom of the container.
第3図は水槽2の断面図である。図において、20は流
入管で、周囲に流入口21があけられ、水槽底22の中
央から水槽中へ突出している。前記流入管20の外周に
は固定床19が水槽底22の前面にわたって敷き詰めら
れている。23は固定床19に繁殖条件の異なる細菌が
同時に繁殖できるようにする固定床分割手段である0本
実施例では、固定床19を中央固定床24側には好気性
細菌25が、外周固定床26側には嫌気細菌27が培養
されるようになっている。28は固定床19と水槽2の
敷石29とを分割する仕切手段である。仕切手段28は
、固定床24の上には開口面積が広い通水口29が、固
定床26の上には開口面積が狭い通水口30があけられ
ている。この開口面積を変えることにより固定床の流速
パター−ン(流量、流速分布)が細菌の繁殖に適する流
れパターンになっている。FIG. 3 is a sectional view of the water tank 2. In the figure, reference numeral 20 denotes an inflow pipe, which has an inlet 21 around it and projects from the center of the tank bottom 22 into the tank. A fixed bed 19 is spread around the outer periphery of the inflow pipe 20 over the front surface of the tank bottom 22. 23 is a fixed bed dividing means that allows bacteria with different breeding conditions to breed simultaneously on the fixed bed 19. In this embodiment, the aerobic bacteria 25 are placed on the central fixed bed 24 side of the fixed bed 19, and the aerobic bacteria 25 are placed on the peripheral fixed bed side. Anaerobic bacteria 27 are cultured on the 26 side. 28 is a partition means for dividing the fixed bed 19 and the paving stones 29 of the water tank 2. In the partition means 28, a water inlet 29 with a wide opening area is provided above the fixed bed 24, and a water inlet 30 with a narrow opening area is provided above the fixed bed 26. By changing this opening area, the flow velocity pattern (flow rate, flow velocity distribution) of the fixed bed becomes a flow pattern suitable for bacterial growth.
固定床として高炉水砕を原料としたサドルロック型セラ
ミックスを用いた。この高炉水砕は製鉄所の溶鉱炉から
溶鉄1.0トン当たり0.5トン発生するスラグを急冷
して製造され、主にセメントの原料や土壌改良材として
使用されているものである。高炉水砕は多孔質のガラス
質でCab、SiOx、AI!Osを主成分とし、この
ほかMgO。Saddle rock type ceramics made from blast furnace granulation was used as the fixed bed. This granulated blast furnace is produced by rapidly cooling 0.5 tons of slag generated per 1.0 tons of molten iron from blast furnaces in steel plants, and is mainly used as a raw material for cement and as a soil improvement material. Blast furnace granulation is porous and glassy, including Cab, SiOx, and AI! The main component is Os, in addition to MgO.
FeOなどを含んでいる。Contains FeO etc.
上記構成において、循環ポンプ10を運転する。In the above configuration, the circulation pump 10 is operated.
水槽1中の魚の排泄物や食べ残しの餅などの有機物、及
び有機物から発生するアンモニアや硝酸塩を含んだ水槽
水は、仕切手段28の通水口29.30を通り水槽1の
底部の固定床19に入り、そこで大きな排泄物や有機物
が捕集され、流入口21から流入管20に流れる。大き
な混入物が取り除かれた水槽水は、更に流入管20から
流入Ill、電磁弁12を経由し循環ポンプ10に入り
、ポンプで加圧され、酸素供給手段6で吸引された空気
を混入し、第1モジユル4、第2モジユル5、加熱殺菌
ユニット9を通り水槽1へと循環する。この循環系にお
いて、まず浄化ユニット3の機構部品に悪影響を及ぼす
大きな排泄物や有機物が捕集される。ここでフィルター
にかけられた魚の排泄物や食べ残しの餅などの有機物、
及び有機物から発生するアンモニアや硝酸塩を含んだ水
槽水は酸素供給手段6で吸引された空気を混入し第1モ
ジユル4、第2モジユル5に入る。ここで水中の有機物
、及び有機物から発生するアンモニアは、鉱物質の表面
に最初から付着している人工的に培養された好気性細菌
、随意性細菌、およびそれらの活性化物質と酸素供給手
段6で吸引された空気中に含まれる酸素とにより酸化分
解され硝酸塩になる。このアンモニアの硝酸塩への酸化
分解反応は次に示す反応式で表される。Organic matter such as fish excrement and leftover rice cake in the aquarium 1, as well as aquarium water containing ammonia and nitrates generated from the organic matter, passes through the water inlets 29 and 30 of the partition means 28, and passes through the fixed bed 19 at the bottom of the aquarium 1. There, large excreta and organic matter are collected and flowed from the inlet 21 to the inlet pipe 20. The aquarium water from which large contaminants have been removed further enters the circulation pump 10 via the inflow pipe 20 and the solenoid valve 12, is pressurized by the pump, and is mixed with air sucked by the oxygen supply means 6. The water passes through the first module 4, the second module 5, and the heat sterilization unit 9 and circulates to the water tank 1. In this circulation system, first, large excreta and organic substances that have an adverse effect on the mechanical parts of the purification unit 3 are collected. Organic matter such as fish excrement and leftover rice cake is filtered here.
The aquarium water containing ammonia and nitrates generated from organic matter is mixed with air sucked in by the oxygen supply means 6 and enters the first module 4 and the second module 5. Here, organic matter in water and ammonia generated from organic matter are derived from artificially cultured aerobic bacteria, voluntary bacteria, their activators, and oxygen supply means 6, which are attached to the surface of mineral materials from the beginning. It is oxidized and decomposed into nitrates by the oxygen contained in the air sucked in. This oxidative decomposition reaction of ammonia to nitrate is expressed by the following reaction formula.
N Ha” + 1.50! N O!−+ HzO
+ H’ ■N Ox−+0.50x〜No、
・・・・・・・・ ■つぎに、この硝酸塩に分解された
成分を含んだ水は、加熱殺菌ユニット9から水槽1に戻
り、水槽l中で発生したを機動やアンモニアと共に、再
び水槽1の底に向かう。N Ha” + 1.50! N O!-+ HzO
+ H' ■N Ox-+0.50x~No,
・・・・・・・・・ ■Next, the water containing the components decomposed into nitrates returns from the heat sterilization unit 9 to the aquarium 1, and is returned to the aquarium 1 together with the water and ammonia generated in the aquarium. heading to the bottom.
この循環がくり返され、日数が経つに従い水槽lの床の
固定床19に細菌が繁殖されてくる。即ち、流量が多く
酸素の供給が多い中央固定床25には好気性細菌が、流
量が少なく酸素の供給が殆どない外周固定床2Gには嫌
気性細菌がそれぞれ繁殖してくる。この結果、硝酸塩に
分解された成分と、水槽1中で発生したを機動やアンモ
ニアを含んだ水槽水は、前記中央固定床25へ流れ込む
と前述したアンモニアが硝酸塩へ酸化分解され、前記外
周固定床26へ流れ込むと、嫌気性細菌によって循環水
中の有機物から発生する水素の作用により、窒素と水と
に分解される。この分解反応は次の式で表される。This cycle is repeated, and as days pass, bacteria are propagated on the fixed bed 19 on the floor of the aquarium l. That is, aerobic bacteria breed in the central fixed bed 25 where the flow rate is high and a large amount of oxygen is supplied, and anaerobic bacteria breed in the peripheral fixed bed 2G where the flow rate is low and almost no oxygen is supplied. As a result, when the aquarium water containing components decomposed into nitrates and ammonia generated in the aquarium 1 flows into the central fixed bed 25, the ammonia is oxidized and decomposed into nitrates, and the ammonia is oxidized and decomposed into nitrates. 26, it is decomposed into nitrogen and water by the action of hydrogen generated from organic matter in the circulating water by anaerobic bacteria. This decomposition reaction is expressed by the following formula.
N O3−+ A H−+Ht 十〇g ・・・・・
・・・■このようにして水槽1中の魚の排泄物や食べ残
しの餌などの有機物、及び有機物から発生するアンモニ
アや硝酸塩を含んだ水槽水は浄化される。N O3-+ A H-+Ht 10g...
...■ In this way, organic matter such as fish excrement and uneaten food in the aquarium tank 1, as well as aquarium water containing ammonia and nitrates generated from the organic matter, are purified.
又、水槽】の中に繁殖した魚の病原菌は前記加熱殺菌ユ
ニット9の紫外線で殺菌される。更に、前記加熱殺菌ユ
ニット9は循環水中の遊離塩素を除去する作用も有し、
魚の飼育環境をより高める働きをしている。Furthermore, pathogenic bacteria on fish that have grown in the aquarium are sterilized by the ultraviolet rays of the heat sterilization unit 9. Furthermore, the heat sterilization unit 9 also has the function of removing free chlorine in the circulating water,
It works to improve the breeding environment for fish.
以上のように、原水中に含まれている遊離塩素や、水槽
Iの中に発生した有機物やアンモニア、魚の病原菌など
は、鉱物質の表面に付着した人工的に培養した細菌群と
酸素により分解されたり、紫外線ランプ23で殺菌され
る。きれいになった水は、流出&8I3を通りアエセパ
レータ14に入り、そこで混入している極微細気泡が成
長して水槽Iに戻る。As mentioned above, free chlorine contained in raw water, organic matter and ammonia generated in aquarium I, pathogenic bacteria for fish, etc. are decomposed by artificially cultured bacterial groups attached to the surface of mineral materials and oxygen. or sterilized with an ultraviolet lamp 23. The clean water passes through the outflow &8I3 and enters the ae separator 14, where the ultrafine bubbles mixed therein grow and return to the aquarium I.
一方、前述の酸素供給手段6は供給ノズル27で形成さ
れたジェット噴流により空気吸引口28より大気を敷用
、空気を循環水中に送りこむ、ここで、吸引された空気
中の酸素の量を■、■式のアンモニアの酸化分解に必要
な量より多くすれば、酸素を多く含んだ水が水槽lに戻
る。その結果、従来の水槽のように散気管を入れて空気
ポンプで常にエアレーションをする必要がなくなる。On the other hand, the above-mentioned oxygen supply means 6 uses the jet stream formed by the supply nozzle 27 to spread the atmosphere from the air suction port 28 and send the air into the circulating water. If the amount is greater than that required for the oxidative decomposition of ammonia in formula (2), oxygen-rich water will return to the tank 1. As a result, unlike traditional aquariums, there is no need to install an aeration pipe and constantly aerate the tank with an air pump.
鉱物質として使用される高炉水砕は多孔質のガラス質で
第1表に示すようにCab、Sin、。Blast furnace granules used as mineral materials are porous and vitreous, and as shown in Table 1, they are classified as Cab, Sin, etc.
A1.O,を主成分とし、このほかMgO,FeOなど
を含んでいる。この主成分であるCaOは、前述の第2
モジユル5でのアンモニアの酸化分解時に発生するH”
(反応式■、■)に対し中和反応をおこない、水[
1内の水のPH値の低下を押さえる働きをする。A1. The main component is O, and also contains MgO, FeO, etc. This main component, CaO, is the second
H generated during oxidative decomposition of ammonia in module 5
A neutralization reaction is performed on (reaction formulas ■, ■), and water [
It works to suppress the drop in the pH value of the water in the water.
表 高炉水砕の組成(%)
CaO5ins Alt03MgOFeOその他43
.3 33.3 14.1 ?、1 0.7 1
.5更に、CaOなどを主成分とする鉱物質の表面には
、水中でカルシウム等の2価のプラスイオンが沢山存在
する。これは、細菌群が一般にはマイナスに帯電されて
いることから、プラスイオンで表面が覆われる前記鉱物
質は、人工的に培養した細菌群や酸素の最適な固定床と
なる。Table Composition of blast furnace granulated water (%) CaO5ins Alt03MgOFeO Others 43
.. 3 33.3 14.1? ,1 0.7 1
.. 5 Furthermore, many divalent positive ions such as calcium are present in water on the surface of mineral substances mainly composed of CaO and the like. This is because bacteria are generally negatively charged, so the mineral material whose surface is covered with positive ions serves as an optimal fixed bed for artificially cultured bacteria and oxygen.
発明の効果
(1)魚飼育水槽の底部に細菌を繁殖させる固定床が置
かれているため、さかなの排泄物や食べ残しの餌などの
有機物は水槽底部の細菌固定床に捕獲され、細菌により
徐々に分解され、水中に溶解する。この結果、循環回路
に挿入された循環ポンプ、空気供給手段、を磁弁等の機
能部品が漬物や食べ残しの餌により動作不能となること
を防ぐことができる。Effects of the invention (1) Since a fixed bed for breeding bacteria is placed at the bottom of the fish tank, organic matter such as fish excrement and uneaten food is captured by the bacteria fixed bed at the bottom of the tank and is It gradually decomposes and dissolves in water. As a result, it is possible to prevent functional parts such as a circulation pump, an air supply means, and a magnetic valve inserted into the circulation circuit from becoming inoperable due to pickles or uneaten food.
また、フィルターを用いた場合に生ずるフィルターの目
詰まりによる動作不能や、それを防止するためのフィル
ター掃除の煩わしさなどが解消できる。Further, it is possible to eliminate the inoperability due to filter clogging that occurs when a filter is used, and the trouble of cleaning the filter to prevent this.
(2)水槽底部の固定床にも細菌の浄化作用があるため
、循環回路中に挿入された浄化モジュールの容量が小さ
くなり、浄化ユニットがコンパクトになる。(2) Since the fixed bed at the bottom of the aquarium also has a bacterial purification effect, the capacity of the purification module inserted into the circulation circuit becomes smaller, making the purification unit more compact.
(3)各水浄化モジュル内に配設される細菌の固定床と
して、CaOを多く含んだ高炉水砕のサドル型セラミッ
クが使用されているので、水槽中の水はアンモニアが分
解し酸が生成しても、PHが減少し酸性側に移ることが
ない、したがって、従来のように、水槽水中へアルカリ
を加えて水を中和することが不必要となる。(3) As a fixed bed of bacteria installed in each water purification module, a saddle-shaped ceramic made of blast furnace granulation containing a large amount of CaO is used, so ammonia decomposes in the water in the water tank and acid is generated. However, the pH does not decrease and shift to the acidic side. Therefore, it is no longer necessary to neutralize the water by adding alkali to the aquarium water as in the past.
(4) 水浄化モジュルの上流にイジェクタ−作用で
大気を吸引する酸素供給手段を配設し、前記浄化モジュ
ルで必要とされる酸素量よりも多くの酸素量が供給され
るように吸引空気量を設定することにより、水槽中の水
は酸素が十分溶存された状態となっている。そのため、
従来のように水槽中へ散気管を挿入し、空気ポンプで常
にエア細菌は死滅することがなく、水槽中に発生する有
機物やアンモニアを運転開始時から分解することができ
る。また、紫外線は魚の病原菌を殺菌するので、魚が病
気で死ぬのを防止することができる。(4) An oxygen supply means for sucking atmospheric air by an ejector action is arranged upstream of the water purification module, and the amount of suction air is adjusted so that a larger amount of oxygen is supplied than the amount of oxygen required by the purification module. By setting , the water in the aquarium has enough oxygen dissolved in it. Therefore,
Unlike conventional systems, an air diffuser tube is inserted into the aquarium and air pumps are used to constantly kill bacteria, and the organic matter and ammonia generated in the aquarium can be decomposed from the start of operation. In addition, UV rays can kill pathogenic bacteria in fish, which can prevent fish from dying from disease.
第1図は本発明の一実施例を示す水浄化装置の外観斜視
図、第2図は同装置の構成原理図、第3図は同装置の浄
化ユニットの断面図、第4図は同接続フランジの断面図
、第5図は従来の水浄化用微生物処理槽の外観分解斜視
図である。
3・・・・・・水浄化ユニット、4・・・・・・第1モ
ジユル、5・・・・・・第2モジユル、6・・・・・・
酸素供給手段、7・・・・・・接合フランジユニット、
8・・・・・・温水加熱ユニット、9・・・・・・紫外
線殺菌ユニット。
代理人の氏名 弁理士 小鍜治 明 ばか2名−蒙 t
モ
ル
h ryt 子 を覧
第
図
U
第
図
第
図Fig. 1 is an external perspective view of a water purification device showing an embodiment of the present invention, Fig. 2 is a diagram of the principle of construction of the device, Fig. 3 is a sectional view of the purification unit of the device, and Fig. 4 is the same connection. A sectional view of the flange, and FIG. 5 is an exploded perspective view of the appearance of a conventional microbial treatment tank for water purification. 3... Water purification unit, 4... First module, 5... Second module, 6...
Oxygen supply means, 7... joint flange unit,
8... Hot water heating unit, 9... Ultraviolet sterilization unit. Agent's name Patent attorney Akira Okaji Two idiots
Claims (5)
循環流路と、底部に流出路を有した水槽と、前記水槽の
底部に置かれた細菌固定床とからなる水浄化装置。(1) A water purification device consisting of a forced circulation passage provided with a water pressure feeding means for circulating water in the aquarium, an aquarium having an outflow path at the bottom, and a fixed bacteria bed placed at the bottom of the aquarium.
分割手段により繁殖条件が相異なる細菌を同時に繁殖で
きるように細菌固定床を複数子に分割した構成とした特
許請求の範囲第1項記載の水浄化装置。(2) The fixed bacterial bed has a fixed bed dividing means, and the fixed bed dividing means divides the bacterial fixed bed into a plurality of cells so that bacteria with different breeding conditions can be simultaneously propagated. The water purification device according to item 1.
循環流路と、底部に流出路を有した水槽と、前記水槽の
底部に置かれた細菌固定床と、及び前記細菌固定床の上
面に設けた仕切手段とからなる水浄化装置。(3) a forced circulation passage provided with a water pressure feeding means for circulating water in the aquarium; an aquarium having an outflow path at the bottom; a bacteria fixed bed placed at the bottom of the aquarium; and the bacteria fixed bed. A water purification device consisting of a partition means provided on the top surface of the water purifier.
が形成される如く、流水抵抗抵抗が異なる複数個のブロ
ックに分割された構成とした特許請求の範囲第3項記載
の水浄化装置。(4) The water purification device according to claim 3, wherein the partitioning means is configured to be divided into a plurality of blocks having different flow resistance so that the flow of the fixed bed is divided into a plurality of blocks having different flow velocity patterns. .
、MgO、FeOが主成分である鉱物質からなる特許請
求の範囲第1項記載の水浄化装置。(5) Fixed bed is CaO, SiO_2, Al_2, O_3
The water purification device according to claim 1, which is made of a mineral material whose main components are , MgO, and FeO.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2238402A JPH04118098A (en) | 1990-09-06 | 1990-09-06 | Water purifier |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2238402A JPH04118098A (en) | 1990-09-06 | 1990-09-06 | Water purifier |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH04118098A true JPH04118098A (en) | 1992-04-20 |
Family
ID=17029671
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2238402A Pending JPH04118098A (en) | 1990-09-06 | 1990-09-06 | Water purifier |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH04118098A (en) |
-
1990
- 1990-09-06 JP JP2238402A patent/JPH04118098A/en active Pending
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