JP3964525B2 - Antibacterial and anti-algae granular material - Google Patents

Antibacterial and anti-algae granular material Download PDF

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Publication number
JP3964525B2
JP3964525B2 JP34565097A JP34565097A JP3964525B2 JP 3964525 B2 JP3964525 B2 JP 3964525B2 JP 34565097 A JP34565097 A JP 34565097A JP 34565097 A JP34565097 A JP 34565097A JP 3964525 B2 JP3964525 B2 JP 3964525B2
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Prior art keywords
wastewater
sludge
water
algae
antibacterial
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JP34565097A
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JPH11138196A (en
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美幸 徳田
慶泰 石山
肇 二渡
治男 海野
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株式会社日本水処理技研
株式会社日立空調Se
丸は工業株式会社
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  • Treatment Of Sludge (AREA)

Description

【0001】
【産業上の利用分野】
本発明は、主としてクーリングタワー冷却水を初め中水道等の水中に浸漬させることにより、これら水中に混在する菌類や藻類の繁殖、繁茂を防止するための抗菌防藻粒状材に関する。
【0002】
【従来技術】
生活廃水や一般産業廃水は、所要の排水基準となるよう廃水処理が施されたうえ排水がなされるもので、生活廃水や一般産業廃水の廃水処理にはその水質や処理コストの面から、生物化学処理や該生物化学処理に加えて凝集沈澱等を付加させて固液分離がなされているため、多量の廃水スラッジが発生する。
従来においてはこの多量に発生する廃水スラッジは、専ら産業廃棄物処理業者に廃棄を委ねていたものであるが、近年においては海上投棄の禁止や内陸においても廃棄場所の著しい制限と、有害物質の浸出に伴う二次公害の発生危険とが相俟って産廃コストも高騰化しており、かかることから生産業者には経営コストの圧迫ばかりか将来に亘っての生産活動も危惧される状況にある。
【0003】
これがため生産者においては、廃水スラッジをフィルタープレス等の機械的手段を用いて該廃水スラッジ中に多量に含有される水分を脱水し、或いは該廃水スラッジを加熱乾燥させることにより減量減嵩化を図っているものの、生産に伴う廃水の絶対量は大なものであるから、仮令機械的手段や加熱手段を用いて減量化減嵩化を図ったところで経営コストの圧迫や廃棄の問題解決には至らない。
【0004】
他方今日においては省エネルギー化、省資源化が産業活動のうえから重要な課題とされており、これがため事務所や店舗或いは生産工場等においても、多量に使用する冷房用の冷却水を循環再利用したり、一旦利用した上水を再浄化して飲用以外の用途に利用する所謂中水道が急速に普及しつつある。
しかしながら、これら循環水や中水道水には細菌類や黴菌類が多量に繁殖するばかりか病菌類も混在し、特にレジオネラ菌等が繁殖して度々死亡事故等重大な結果が招来されている。
更に該循環水や中水道水にはアオミドロを初めとする藻類の発生並びに繁茂も招来されるため、これが循環器機や配管内に付着して閉塞事故が惹起されたり、或いは噴水池内等に付着し水景を損ねたりする問題を抱えている。
【0005】
発明者等はかかる問題に鑑み鋭意研究を重ねた結果、有機物を含む生活廃水や一般産業廃水を廃水処理して排出される廃水スラッジを、その温度が300乃至800℃で焼成させることにより含有された多量の水分や揮発分の蒸散及び揮散に伴い多孔質に形成され且有機物が炭化物化し、而もその組成成分が概ね酸化珪素45乃至55%、酸化アルミニウム20乃至25%、酸化鉄3乃至4.5%、酸化カルシウム3乃至4.5%、酸化マグネシウム2乃至3%、酸化カリウム1.9乃至2.8%、酸化硫黄1.6乃至2.5%その他酸化リン、酸化ナトリウム等1.2乃至1.6%重量割合からなる焼成スラッジ塊が形成されること、並びにこの焼成スラッジ塊を所要の大きさに破砕のうえ900乃至1100℃で更に二次焼成することにより酸化珪素の熔化に伴い炭化物が焼去され且硬化に伴い強硬な粒状体が形成しえること、及びかかる粒状体の外表面や多孔内面にオリゴダイナミック作用を保持する銀若しくは銅を均質に担持させることにより、水中に混在する菌類の抗菌並びに藻類の防藻が効果的に且長期に亘ってなしえることを究明し本発明に至った。
【0006】
【発明が解決しようとする課題】
即ち本発明は菌類や藻類の混在する循環水や中水の流路に浸漬し接触させることにより、菌類に対する抗菌並びに藻類に対する防藻が効果的且長期に亘ってなしえ、而も極めて安価な抗菌防藻粒状材を提供することにある。
【0007】
【課題を解決するための手段】
上述の課題を解決するために本発明が採用した技術的手段は、有機物を含む生活廃水や一般産業廃水を廃水処理することにより排出される廃水スラッジを、300乃至800℃の温度で焼成することにより多量に含水された水分や含有されてなる揮発分を蒸散並びに揮散させることにより多数の微孔が形成された多孔性の焼成スラッジ塊となしたうえ所要の大きさに破砕し、而して所要の大きさに破砕された多孔性の焼成スラッジを900乃至1100℃の温度で二次焼成させることにより、炭化物を焼去し且酸化珪素の熔化により硬化させ而も且組成成分相互が固定された粒状体を形成し、この粒状体の外表面及び多孔内面に銀若しくは銅を均質に担持させてなる構成に存する。
【0008】
【作用】
本発明は上述の如き構成からなるため、以下のような作用を有する。即ち有機物を含む生活廃水や一般産業廃水を廃水処理して排出される廃水スラッジには、略70乃至90%程度の水分が含水されてなるばかりか油脂分を初めとする揮発分も含有されてなるものの、この廃水スラッジを300乃至800℃の温度で焼成させることで水分や揮発分の蒸散や揮散に伴って乾燥固化が図れるとともに、水分や揮発分の蒸散や揮散に伴い多数の微孔が形成され、且有機物が炭化した炭化物の混在する多孔性の焼成スラッジ塊が形成される。
而してこの焼成スラッジ塊を所要の大きさに破砕したうえ、900乃至1100℃の温度で二次焼成をなすため、炭化物が焼去されるとともに酸化珪素が熔化して組成成分相互が固定されて強硬な粒状体が形成される。
そしてかかる粒状体の表面や多孔内面に銀若しくは銅が均質に担持されてなるため、菌類や藻類の混在する循環水や中水中に浸漬させることにより、大きな接触面積を以って循環水や中水と接触し、而もその接触面より銀や銅のオリゴダイナミック作用が働くため、菌類に対する抗菌及び藻類に対する防藻効果が発揮される。
【0009】
【実施例】
以下に本発明実施例を詳細に説明すれば、本発明に用いる廃水スラッジは生活廃水や一般産業廃水の如く有機物が混在する廃水を生物化学処理により或いは該生物化学処理に凝集沈澱処理を併用して廃水処理を施し、以って排出される廃水スラッジを用いるもので、かかる廃水スラッジには略70乃至90%重量の水分が含水されている。
【0010】
そしてかかる如き水分率の高い廃水スラッジを乾燥固化させ且その接触表面積を大きく所謂多数の微孔を形成させるため300乃至800℃の温度範囲で焼成させるものであるが、かかる場合の焼成温度は使用する廃水スラッジの水分率や、乾燥固化に伴い形成される接触表面積所謂微孔の大きさ及びその数等によって異り、且実用に際しては略同等粒径のものを用いる関係上からも、無定形で且乱雑な大きさに乾燥固化されることを避けねばならない。
これがためには、その水分率が略70乃至90%重量と高い廃水スラッジの場合では焼成に際して成可く低温度、望ましくは300乃至400℃程度の範囲で水分や揮発分の蒸散或いは揮散を緩やかになすことが、乾燥固化に伴う塊状物の形成のうえから望まれる。
【0011】
他方廃水スラッジをフィルタープレス等により脱水し、その含水率が略50乃至70%程度まで脱水されてなる廃水スラッジを使用する場合では、廃水スラッジが粘性を保持するため十分に高温度で焼成し、内部の水分や揮発分を急激に蒸散或いは揮散させて多数の微孔を形成させながら塊状の焼成スラッジ塊を形成することが出来る。
【0012】
ところで本発明の使用方法は略同等の粒径に形成された本発明を、クーリングタワー循環水や中水道等の流路内に浸漬させて接触流通させ、そのオリゴダイナミック作用により抗菌や防藻を図るものであるから、形成された焼成スラッジ塊を予め所要の粒径に破砕する必要がある。かかる場合において実用に供する本発明の粒径は略5mm程度から最大30mm程度の物が通常使用されるものであるから、焼成スラッジ塊の破砕も略この程度の粒径に破砕されることとなる。
破砕の方法に際しては特段の制約はないが、本発明は球形状で使用されることが望まれることから、該焼成スラッジ塊の破砕も成可く球形に近い形状で破砕することが好都合であって、これがため通常はボールミル等の使用が提案される。
【0013】
かくして所要の粒径に破砕された焼成スラッジは、更に900乃至1100℃の高温度により二次焼成がなされるもので、かかる二次焼成は残留混在する炭化物を焼去せしめるとともに、組成成分の酸化珪素を熔化せしめて実用使用に耐えうる強靭性や硬度を付与せしめるとともに、微量に混在する成分等の不溶化のための固定を図ることによる。
かかる場合における二次焼成の具体的焼成温度や焼成時間等は、焼成スラッジの物性や破砕された粒径或いは要求される強靭性や硬度等によっても異なるが、含水率が60%の廃水スラッジを600℃1時間で焼成させた焼成スラッジ塊を略6mmの粒径に破砕させた焼成スラッジにおいては、二次焼成温度として930乃至950℃、焼成時間として60乃至90分程度が目安となる。
【0014】
二次焼成に際しての焼成方法には特別な制約はないが、焼成スラッジ塊を所要の大きさに破砕した状態においてはその形状も多様なものであるものの、本発明の使用に際しては球形状のものが望まれるため、二次焼成において球形化の図れるものがより好適であって、かかる条件を満たす二次焼成方法の一例を挙げれば、ロータリーキルンの如く加熱炉が傾斜且回転可能に装置された加熱炉の上方より破砕された焼成スラッジを供給し、該加熱炉を転動させつつ焼成することで球形状の粒状体の形成がなしえる。
【0015】
かくして二次焼成がなされて形成された粒状体の表面並びに多孔内面には、その微量金属イオンによる殺菌殺藻作用所謂オリゴダイナミック作用を効果的に且長期に亘って発揮させるための銀若しくは銅が均質に担持されている。
この銀若しくは銅の担持手段も特別な制約はないが、その表面並びに多孔内面に実質的に0.1%重量割合以上の割合で且露出されるよう而も強固に添着されているものであれば実用に供しえる。
本発明においての銀若しくは銅の担持手段として好適なものとしては、銀の担持には予め所要の希釈割合に希釈させてなる硝酸銀溶液を用い、更に銅の担持には硫酸銅を所要の希釈割合に希釈させた硫酸銅溶液を用いて、且これら溶液中に粒状体を浸漬させて硝酸銀溶液若しくは硫酸銅溶液を十分に浸透させたうえ、次いでアルカリ溶液中において硝酸若しくは硫酸を中和させることにより、銀若しくは銅が担持された本発明が形成されることとなる。
【0016】
【発明の効果】
本発明は上述したように、膨大に発生する廃水スラッジを300乃至800℃の温度で焼成するのみで略1/8乃至1/10に減量化減嵩化され、且接触表面積の極めて大きな多孔性の焼成スラッジ塊が形成され、而もこの焼成スラッジ塊を適宜大きさに破砕のうえ900乃至1100℃の温度で二次焼成させるため、残留混在する炭化物が焼去されるとともに、酸化珪素の熔化に伴って強靭化と硬化が図られるばかりか、微量組成成分も固定されて不熔化されるため二次公害の発生危険のない使用安全性の高い粒状体が形成される。
そしてこの粒状体の表面や多孔内面には銀若しくは銅が均質に担持されてなるから菌類や藻類が混在する循環水や中水等の流路に浸漬させるのみで、その大きな表面積から銀若しくは銅のオリゴダイナミック作用が働き、抗菌性や防藻性が効果的的に発揮されるとともに、多孔内面への担持により長期に亘っての抗菌性や防藻性が保持される等多くの特長を具備した抗菌防藻粒状材といえる。
[0001]
[Industrial application fields]
The present invention relates to an antibacterial and anti-algal particulate material for preventing the growth and growth of fungi and algae mixed in water mainly by immersing cooling tower cooling water in water such as a central water supply.
[0002]
[Prior art]
Domestic wastewater and general industrial wastewater are drained after being treated so that they meet the required drainage standards. Living wastewater and general industrial wastewater are treated from the viewpoint of water quality and treatment costs. A large amount of wastewater sludge is generated because solid-liquid separation is carried out by adding agglomeration precipitates in addition to chemical treatment and biochemical treatment.
In the past, this large amount of wastewater sludge was exclusively left to industrial waste disposal companies, but in recent years it has been banned from being dumped at sea, and there are significant restrictions on waste disposal sites, as well as harmful substances. Combined with the risk of secondary pollution due to leaching, industrial waste costs are also rising, and as a result, producers are concerned about not only management costs but also future production activities.
[0003]
For this reason, producers can reduce the weight and volume of wastewater sludge by dehydrating water contained in a large amount in the wastewater sludge using a mechanical means such as a filter press, or by heating and drying the wastewater sludge. Although the absolute amount of wastewater associated with production is large, although it has been attempted to reduce weight and volume using temporary mechanical means and heating means, it is necessary to solve management cost pressure and disposal problems. It does n’t come.
[0004]
On the other hand, energy saving and resource saving are regarded as important issues in industrial activities today, and this makes it possible to recycle and reuse cooling water used in large quantities in offices, stores, and production factories. In other words, so-called water supply for repurifying the once-used water and using it for purposes other than drinking is rapidly spreading.
However, the circulating water and the tap water have not only a large amount of bacteria and gonococci but also pathogenic fungi. In particular, Legionella bacteria and the like have been bred to cause serious consequences such as death.
In addition, the circulating water and the tap water cause the generation and growth of algae such as blue-green algae, and this may adhere to the circulator and the piping and cause a clogging accident, or adhere to the fountain. I have problems that damage the waterscape.
[0005]
As a result of intensive studies in view of such problems, the inventors have included wastewater sludge discharged from wastewater treatment of domestic wastewater and general industrial wastewater containing organic matter by firing at a temperature of 300 to 800 ° C. It is formed to be porous with the evaporation and volatilization of a large amount of water and volatile matter, and the organic matter is carbonized, and its composition components are generally 45 to 55% silicon oxide, 20 to 25% aluminum oxide, and 3 to 4 iron oxide. 0.5%, calcium oxide 3 to 4.5%, magnesium oxide 2 to 3%, potassium oxide 1.9 to 2.8%, sulfur oxide 1.6 to 2.5%, other phosphorus oxides, sodium oxide, etc. Forming a calcined sludge lump having a weight ratio of 2 to 1.6%, crushing the calcined sludge lump to a required size, and further performing secondary firing at 900 to 1100 ° C. Carbide is burned off as silicon oxide melts, and hard particles can be formed as it hardens, and silver or copper holding oligodynamic action is uniformly supported on the outer surface and porous inner surface of such particles. As a result, the present inventors have found that antibacterial fungi and algae-preventing algae mixed in water can be effectively and over a long period of time.
[0006]
[Problems to be solved by the invention]
That is, the present invention can effectively and antibacterial against fungi and algae over a long period of time by being immersed in and brought into contact with circulating water or medium water flow channels in which fungi and algae are mixed, and is extremely inexpensive. The object is to provide an antibacterial and anti-algae granular material.
[0007]
[Means for Solving the Problems]
The technical means adopted by the present invention in order to solve the above-mentioned problem is to burn wastewater sludge discharged by treating wastewater containing organic matter and general industrial wastewater at a temperature of 300 to 800 ° C. By transpiration and volatilization of the moisture contained in a large amount of water and the contained volatile matter, it became a porous calcined sludge mass formed with many micropores and then crushed to the required size, thus Porous calcined sludge crushed to the required size is secondarily calcined at a temperature of 900 to 1100 ° C. to burn off the carbide and harden it by melting silicon oxide, and the components are fixed to each other. In this configuration, silver or copper is uniformly supported on the outer surface and the porous inner surface of the granular material.
[0008]
[Action]
Since the present invention is configured as described above, it has the following effects. In other words, wastewater sludge discharged from wastewater treatment of domestic wastewater and general industrial wastewater containing organic substances contains not only about 70 to 90% of water but also volatile components such as fats and oils. However, by firing this wastewater sludge at a temperature of 300 to 800 ° C., it is possible to dry and solidify with the transpiration and volatilization of moisture and volatile components, and there are many micropores with the transpiration and volatilization of moisture and volatile components. A porous fired sludge lump is formed which is formed and contains a mixture of carbides obtained by carbonizing organic substances.
Thus, this calcined sludge lump is crushed to a required size and subjected to secondary firing at a temperature of 900 to 1100 ° C., so that the carbide is burned off and silicon oxide is melted to fix the composition components to each other. And a hard granular body is formed.
And since silver or copper is uniformly supported on the surface of the granular material or the porous inner surface, it is possible to circulate water or medium with a large contact area by immersing it in circulating water or middle water mixed with fungi and algae. Since it comes into contact with water and the oligodynamic action of silver and copper works from its contact surface, it exhibits antibacterial effects against fungi and an algal control effect against algae.
[0009]
【Example】
In the following, the embodiment of the present invention will be described in detail. The wastewater sludge used in the present invention is a wastewater mixed with organic matter such as domestic wastewater or general industrial wastewater by biochemical treatment or combined with coagulation sedimentation treatment in the biochemical treatment. The wastewater sludge discharged and then discharged is used, and the wastewater sludge contains about 70 to 90% by weight of water.
[0010]
The waste water sludge having such a high moisture content is dried and solidified, and the contact surface area is increased and a large number of so-called micropores are formed. In this case, the firing temperature is used. It varies depending on the water content of wastewater sludge, the contact surface area formed by drying and solidification, the size and number of micropores, etc. It must be dried and solidified to a messy size.
For this purpose, in the case of wastewater sludge having a high moisture content of about 70 to 90% by weight, the transpiration or volatilization of moisture and volatile matter is moderated at a low temperature that can be achieved during firing, preferably in the range of about 300 to 400 ° C. It is desirable from the viewpoint of formation of a lump accompanying dry solidification.
[0011]
On the other hand, when wastewater sludge is dehydrated with a filter press or the like and the wastewater sludge whose water content is dehydrated to about 50 to 70% is used, the wastewater sludge is baked at a sufficiently high temperature to maintain the viscosity, A massive calcined sludge mass can be formed while rapidly evaporating or evaporating internal moisture and volatile matter to form a large number of micropores.
[0012]
By the way, the method of use of the present invention is to immerse the present invention formed in substantially the same particle size in a flow path such as cooling tower circulating water or waterworks and to circulate it, and to achieve antibacterial and algal protection by its oligodynamic action. Since it is a thing, it is necessary to grind | pulverize the baking sludge lump formed to a required particle size beforehand. In such a case, the particle size of the present invention for practical use is usually about 5 mm to a maximum of about 30 mm, so the crushed sludge lump is also crushed to a particle size of this level. .
Although there are no particular restrictions on the crushing method, since it is desired that the present invention is used in a spherical shape, it is convenient to crush the calcined sludge mass in a shape close to a spherical shape. For this reason, the use of a ball mill or the like is usually proposed.
[0013]
Thus, the calcined sludge crushed to the required particle size is further subjected to secondary calcining at a high temperature of 900 to 1100 ° C. This secondary calcining burns away residual carbides and oxidizes the composition components. By melting silicon to impart toughness and hardness that can withstand practical use, and fixing for insolubilization of components and the like mixed in trace amounts.
In such a case, the specific firing temperature, firing time, etc. of the secondary firing differ depending on the physical properties of the fired sludge, the crushed particle size, required toughness, hardness, etc., but waste water sludge having a moisture content of 60% is used. In a calcined sludge obtained by crushing a calcined sludge mass calcined at 600 ° C. for 1 hour to a particle size of about 6 mm, a secondary calcining temperature of 930 to 950 ° C. and a calcining time of about 60 to 90 minutes are a standard.
[0014]
There are no particular restrictions on the firing method in the secondary firing, but the shape of the sludge lump is various in the state of being crushed to the required size, but in the use of the present invention is a spherical shape Therefore, it is more preferable that the spheroidization can be performed in the secondary firing. An example of the secondary firing method satisfying such a condition is as follows. Spherical granulates can be formed by supplying the smashed sludge from above the furnace and firing it while rolling the heating furnace.
[0015]
Thus, the surface of the granular body formed by the secondary firing and the porous inner surface have silver or copper for effectively and long-terming the so-called oligodynamic action of the bactericidal and algicidal action by the trace amount of metal ions. It is supported uniformly.
The silver or copper supporting means is not particularly limited, but it may be firmly attached to the surface and the porous inner surface so as to be substantially exposed at a ratio of 0.1% by weight or more. Can be put to practical use.
As a silver or copper supporting means suitable for the present invention, a silver nitrate solution previously diluted to a required dilution ratio is used for supporting silver, and copper sulfate is further used for supporting copper. By immersing the granular material in these solutions to sufficiently infiltrate the silver nitrate solution or the copper sulfate solution, and then neutralizing the nitric acid or sulfuric acid in the alkaline solution. Thus, the present invention carrying silver or copper is formed.
[0016]
【The invention's effect】
As described above, according to the present invention, the waste water sludge generated in large quantities is reduced to approximately 1/8 to 1/10 only by firing at a temperature of 300 to 800 ° C., and has a very large contact surface area. The calcined sludge lump is formed, and the calcined sludge lump is crushed to an appropriate size and secondarily fired at a temperature of 900 to 1100 ° C., so that residual carbides are burned out and silicon oxide is melted. Along with this, not only toughening and hardening are achieved, but also a small amount of composition components are fixed and insolubilized, so that a highly safe granular material free from the risk of secondary pollution is formed.
And since silver or copper is uniformly supported on the surface of the granular material or the porous inner surface, it is simply immersed in a flow path such as circulating water or middle water in which fungi and algae are mixed. It has many features such as anti-dynamic and anti-algae properties are effectively exhibited, and anti-bacterial and anti-algae properties are maintained for a long time by being supported on the porous inner surface. It can be said that it is an antibacterial and alga-proof granular material.

Claims (1)

生活廃水若しくは一般産業廃水の廃水処理に際して排出される廃水スラッジを、300乃至800℃の温度で焼成させて多孔性焼成スラッジ塊となし且これを所要の大きさに破砕し、而して900乃至1100℃の温度で二次焼成することにより炭化物の焼去と硬化を図ったうえ、銀若しくは銅を少なくとも0.1%重量以上の割合でその表面及び多孔内面に均質に担持させてなることを特徴とする抗菌防藻粒状材。Wastewater sludge discharged during wastewater treatment of domestic wastewater or general industrial wastewater is calcined at a temperature of 300 to 800 ° C. to form a porous calcined sludge mass, which is crushed to a required size, and thus 900 to 900 Carbide is burned out and hardened by secondary firing at a temperature of 1100 ° C., and silver or copper is uniformly supported on the surface and porous inner surface at a ratio of at least 0.1% by weight. Antibacterial and anti-algae granular material.
JP34565097A 1997-11-11 1997-11-11 Antibacterial and anti-algae granular material Expired - Fee Related JP3964525B2 (en)

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