JPH0155914B2 - - Google Patents
Info
- Publication number
- JPH0155914B2 JPH0155914B2 JP57112479A JP11247982A JPH0155914B2 JP H0155914 B2 JPH0155914 B2 JP H0155914B2 JP 57112479 A JP57112479 A JP 57112479A JP 11247982 A JP11247982 A JP 11247982A JP H0155914 B2 JPH0155914 B2 JP H0155914B2
- Authority
- JP
- Japan
- Prior art keywords
- medium
- wastewater
- purification
- septic tank
- crushed
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
- 239000002351 wastewater Substances 0.000 claims description 20
- 238000000746 purification Methods 0.000 claims description 17
- 230000003647 oxidation Effects 0.000 claims description 14
- 238000007254 oxidation reaction Methods 0.000 claims description 14
- 239000011396 hydraulic cement Substances 0.000 claims description 10
- 230000005484 gravity Effects 0.000 claims description 9
- 230000003197 catalytic effect Effects 0.000 claims description 7
- 238000005096 rolling process Methods 0.000 claims description 7
- 239000010881 fly ash Substances 0.000 claims description 6
- 229910021536 Zeolite Inorganic materials 0.000 claims description 4
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims description 4
- 239000000843 powder Substances 0.000 claims description 4
- 239000010457 zeolite Substances 0.000 claims description 4
- 239000008187 granular material Substances 0.000 claims 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 14
- 244000005700 microbiome Species 0.000 description 9
- 239000010865 sewage Substances 0.000 description 9
- 239000004575 stone Substances 0.000 description 9
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 7
- 239000010802 sludge Substances 0.000 description 7
- 238000004140 cleaning Methods 0.000 description 6
- 239000004568 cement Substances 0.000 description 5
- 238000005469 granulation Methods 0.000 description 5
- 230000003179 granulation Effects 0.000 description 5
- 239000000203 mixture Substances 0.000 description 5
- 239000007787 solid Substances 0.000 description 5
- 238000011001 backwashing Methods 0.000 description 4
- 230000000052 comparative effect Effects 0.000 description 4
- 238000002474 experimental method Methods 0.000 description 4
- 238000000034 method Methods 0.000 description 3
- 239000008213 purified water Substances 0.000 description 3
- 239000000377 silicon dioxide Substances 0.000 description 3
- 239000002893 slag Substances 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 239000011398 Portland cement Substances 0.000 description 2
- 238000007664 blowing Methods 0.000 description 2
- 239000010840 domestic wastewater Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000011381 foam concrete Substances 0.000 description 2
- 239000010438 granite Substances 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 101700004678 SLIT3 Proteins 0.000 description 1
- 102100027339 Slit homolog 3 protein Human genes 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 239000011400 blast furnace cement Substances 0.000 description 1
- 210000004556 brain Anatomy 0.000 description 1
- 235000014633 carbohydrates Nutrition 0.000 description 1
- 150000001720 carbohydrates Chemical class 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 230000002349 favourable effect Effects 0.000 description 1
- 239000004088 foaming agent Substances 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 229910010272 inorganic material Inorganic materials 0.000 description 1
- 239000011147 inorganic material Substances 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 150000002632 lipids Chemical class 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 238000005065 mining Methods 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- RMAQACBXLXPBSY-UHFFFAOYSA-N silicic acid Chemical compound O[Si](O)(O)O RMAQACBXLXPBSY-UHFFFAOYSA-N 0.000 description 1
- 235000012239 silicon dioxide Nutrition 0.000 description 1
- 238000011144 upstream manufacturing Methods 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
- Biological Treatment Of Waste Water (AREA)
Description
〔産業上の利用分野〕
本発明は生活排水等で汚れた中小河川の浄化を
効率的に行う浄化媒体に関するものである。
〔従来の技術〕
近年、生活排水などによる中小河川の汚染は甚
だしく、管理者はその河川の浄化に苦慮してい
る。その解決方法の一つとして、汚水の浄化にほ
とんど人工的なエネルギーを必要とせず、生物化
学的酸化作用を巧みに利用した礫間接触酸化法が
最近注目されるようになつてきた。
この礫間接触酸化法による汚水の浄化は、接触
酸化媒体として径が5〜80mm程度の玉石を用い、
この玉石を充填した浄化槽に汚水を通過させ、玉
石の表面に生息する好気性微生物に汚水中の汚濁
物、炭水化物、脂質、蛋白質などを喰わせて汚水
を浄化する方法である。またこの方法によれば、
好気性微生物は嫌気性微生物に比べて約10倍の早
さで溶存アンモニアやリンなどを栄養として食
し、無害の亜硝酸型窒素等に変えることができ
る。そしてこの際、汚水中のSS(浮遊物質)も微
生物が出す粘液によつて捕捉され、無害物質に変
えられることが知られている。
〔発明が解決しようとする課題〕
しかるに近年、河川の上流に洪水調制用ダムが
構築されたために下流の河川敷などに接触酸化媒
体に適した粒度および形状の玉石が不足して来た
ことや、河川敷における玉石の採掘が禁止された
ため、大規模な浄化床を設置するのに苦慮してい
る現状である。そしてこの玉石の不足を補うため
に花こう岩や凝灰岩などを砕いて玉石の代わりに
使用するとか、または高炉スラグ砕石を使用する
方法などが提案されているが、これら天然砕石や
スラグ砕石は玉石と比べ適度の凹凸があるため、
微生物の付着は良好であるが、砕石間の噛合いが
良いために、砕石に付着した汚泥を水で逆洗浄す
るとき、浄化汚泥が完全に除去されず表面に溜ま
りやすく、短期間で目づまりを起こし浄化の目的
が達せられなくなる欠点がある。
本発明は、このような欠点を解消した汚水の接
触酸化浄化媒体を提供することを目的とする。
〔課題を解決するための手段〕
本発明者等は、上記目的を達成するために種々
検討を重ねた結果、特定の骨材と水硬性セメント
とを転動造粒して硬化させた球状媒体は、表面が
粗面をなすため、見掛比重1.0〜2.0粒径が5〜80
mmの球状媒体としてこれを従来の玉石の代わりに
使用して接触酸化浄化槽を造ると、汚水の浄化に
当り微生物の付着が良好になり、浄化速度が大に
なつて浄化効率が向上するばかりでなく、浄化槽
を清水により逆洗浄する場合にも、媒体の比重が
小さいため媒体が洗浄水により浮遊運動して媒体
間の互擦作用により媒体表面から付着汚泥が除去
され易くなるので洗浄時間は短縮され、浄化槽を
長期間繰返えし使用することができることを知見
した。
かかる知見に基づく本発明の汚水の接触酸化浄
化媒体は、フライアツシユ、ゼオライト粉粒体及
びALC破砕物の中から選ばれる1種以上の骨材
と水硬性セメントとを転動造粒して硬化させてな
り、径が5〜80mmの表面が粗の球状体であつて、
見掛比重が1.2〜2.0であることを特徴とする。
ここで「ALC」とは、石灰、セメントなどの
石灰質原料と、けい石、けい砂、スラグ、フライ
アツシユなどのけい酸質原料とを混合粉砕したも
のに適量の水、気泡剤などを添加混合し、多孔質
化したものをオートクレーブ養生によつて硬化さ
せて得た多孔質の軽量気泡コンクリート成形体で
あり、その製品の一つである建築用パネルに関し
てJIS A5416「軽量気泡コンクリートパネル
(ALCパネル)」が制定されている。本発明にお
いて使用するALC破砕物は、このALC成形体を
破砕したものである。
本発明の浄化媒体は多孔質無機材料であるフラ
イアツシユ、ゼオライト粉粒体、ALC破砕物を
骨材として選定し、それに水硬性セメントをバイ
ンダーとして混合したものを転動造粒して球状体
としたものであり、骨材と水硬性セメントとを混
合したものが常に造粒面にまぶされて造粒が行わ
れるために、球状体の表面は適度な粗面を形成
し、且つ多孔質の骨材がまぶされた状態で表面に
存在している。この表面の骨材の多孔面と、表面
の適度な粗面とが相俟つて好気性微生物の生息に
良好な環境を作つており、浄化作用が促進され
る。また転動造粒による表面の粗面は、逆洗浄時
において適度に微生物を残して汚泥を除去するこ
とができるので、逆洗浄が容易に行えると共に、
再使用に際して早期に浄化作用を回復させること
ができる。
以下、本発明を実験に基づいて説明する。
火力発電所から産出されるフライアツシユ(ブ
レーン比表面積2300cm2/g、見掛比重2.13)80Kg
にポルトランドセメント20Kgを加え、この混合物
をパンペレタイザーに投入し水を加えつつ造粒し
て径5〜40mmの球状媒体118Kgを造つた。この媒
体の見掛比重は1.85であつた。
この媒体を第1図に示す如き実験用浄化槽(巾
50cm×50cm、高さ100cm)内に空〓率約25%にな
るように充填した。
なお、図において1は浄化槽、2は浄化槽1の
内に接触酸化媒体を空〓率が25%になるようにス
リツト3上に充填した媒体層である。また4は浄
化槽1の上部に設けた管であつて汚水を浄化する
場合にはこの管から汚水を送入し、浄化された水
は後記の管6より排出する。5は浄化槽1下部に
設けた空気吹込管である。次に6は浄化槽1の下
部に設けた管であつて、接触酸化媒体2に付着し
た汚泥を清水で洗浄する場合にはこの管から清水
を送入し、洗浄に使われた水は上記の管4より排
出する。
次にこの実験用浄化槽1中に汚水送入口4より
BOD30mg/、SS45mg/含有の20℃の汚水を
流量0.85〜8.5/min(滞留時間に換算して4.9〜
0.5時間)の範囲内で送液すると共に、圧縮空気
を20/minの割合で空気吹込口5より吹込み、
浄化水を出口6より排出させた。
なお、この実験にあたり新品の酸化浄化媒体に
予め上記汚水を3時間通し、汚水中の微生物を媒
体上に定着させた後、汚水を注入した。
この実験により得た結果を第2図および第3図
に示す。
また第2図および第3図には、比較例として径
5〜40mm、見掛比重2.53の花こう岩砕石および径
5〜40mm、見掛比重2.40の玉石を第1図と同じ実
験用浄化槽内に上記と同じ空〓率になるように充
填し、上記と同様にして同じ組成の汚水を送液す
ると共に、圧縮空気を吹込んだ結果を併記した。
さらにまた、上記3種の汚水浄化試験を3日間
連続して行つた後、汚水の送液を止め、浄化水入
口6より清水を20/minの割合で送液すると共
に、空気吹込口5より圧縮空気を30/minの割
合で10分間通気して洗浄水を出口4より排出し逆
洗浄したたところ、本発明媒体は砕石媒体および
玉石媒体と異なり、洗浄水により浮遊し互擦運動
したため第1表に示す結果を得た。
[Industrial Application Field] The present invention relates to a purification medium that efficiently purifies small and medium-sized rivers contaminated with domestic wastewater and the like. [Prior Art] In recent years, small and medium-sized rivers have been severely polluted by domestic wastewater, and managers are struggling to purify the rivers. As one solution to this problem, gravel contact oxidation, which requires little artificial energy to purify wastewater and skillfully utilizes biochemical oxidation, has recently attracted attention. Purification of wastewater by this gravel contact oxidation method uses cobblestones with a diameter of about 5 to 80 mm as the contact oxidation medium.
In this method, wastewater is passed through a septic tank filled with these cobblestones, and the aerobic microorganisms that live on the surface of the cobbles eat pollutants, carbohydrates, lipids, proteins, etc. in the wastewater, thereby purifying the wastewater. Also, according to this method,
Aerobic microorganisms can consume dissolved ammonia and phosphorus as nutrients and convert them into harmless nitrite-type nitrogen and other substances about 10 times faster than anaerobic microorganisms. At this time, it is known that suspended solids (SS) in wastewater are also captured by the slime produced by microorganisms and converted into harmless substances. [Problem to be solved by the invention] However, in recent years, as flood control dams have been constructed upstream of rivers, there has been a shortage of cobblestones with particle size and shape suitable for catalytic oxidation media in downstream riverbeds. Since cobblestone mining on riverbeds has been banned, the current situation is that it is difficult to install large-scale purification beds. In order to compensate for this shortage of cobblestone, it has been proposed to use crushed granite or tuff instead of cobblestone, or to use crushed blast furnace slag stone, but these natural crushed stones and crushed slag stones are Because there is moderate unevenness compared to
Although the adhesion of microorganisms is good, due to the good interlocking between the crushed stones, when the sludge adhering to the crushed stones is backwashed with water, the purified sludge is not completely removed and tends to accumulate on the surface, causing clogging in a short period of time. There is a drawback that the purpose of purification cannot be achieved. The object of the present invention is to provide a catalytic oxidation purification medium for wastewater that eliminates these drawbacks. [Means for Solving the Problems] As a result of various studies to achieve the above object, the present inventors have developed a spherical medium made by rolling and granulating specific aggregate and hydraulic cement. Because the surface is rough, the apparent specific gravity is 1.0 to 2.0, and the particle size is 5 to 80.
If a contact oxidation septic tank is constructed using this as a spherical medium of mm size instead of conventional cobblestones, microorganisms will be able to adhere well to the wastewater purification process, and the purification speed will increase, which will only improve the purification efficiency. In addition, even when backwashing a septic tank with clean water, the medium has a small specific gravity, so the medium floats in the wash water, and the interaction between the media makes it easier to remove adhered sludge from the surface of the medium, reducing cleaning time. It was discovered that the septic tank can be used repeatedly for a long period of time. Based on this knowledge, the catalytic oxidation purification medium for wastewater of the present invention is produced by rolling granulating and hardening one or more aggregates selected from fly ash, zeolite powder, and crushed ALC and hydraulic cement. It is a spherical body with a rough surface and a diameter of 5 to 80 mm.
It is characterized by an apparent specific gravity of 1.2 to 2.0. Here, "ALC" is a mixture of calcareous raw materials such as lime and cement and silicic acid raw materials such as silica stone, silica sand, slag, and fly ash, mixed with an appropriate amount of water and a foaming agent. , is a porous lightweight cellular concrete molded product obtained by curing the porous material by autoclave curing, and one of its products, a construction panel, is compliant with JIS A5416 "Lightweight cellular concrete panel (ALC panel)". ' has been enacted. The ALC crushed material used in the present invention is obtained by crushing this ALC molded body. The purification medium of the present invention is made by selecting porous inorganic materials such as fly ash, zeolite powder, and crushed ALC as aggregates, and mixing them with hydraulic cement as a binder, which is then granulated by rolling to form spherical bodies. Because the granulation surface is always sprinkled with a mixture of aggregate and hydraulic cement, the surface of the spherical bodies forms a moderately rough surface and is porous. The surface is covered with aggregate. The porous surface of the aggregate on the surface and the moderately rough surface combine to create a favorable environment for aerobic microorganisms to inhabit, promoting the purification effect. In addition, the rough surface created by rolling granulation allows sludge to be removed while leaving an appropriate amount of microorganisms during backwashing, making backwashing easy and
The purifying effect can be quickly restored upon reuse. The present invention will be explained below based on experiments. Fly ash produced from a thermal power plant (Brain specific surface area 2300cm 2 /g, apparent specific gravity 2.13) 80Kg
20 kg of Portland cement was added to the mixture, and this mixture was put into a pan pelletizer and granulated while adding water to produce 118 kg of spherical media with a diameter of 5 to 40 mm. The apparent specific gravity of this medium was 1.85. This medium was used in an experimental septic tank (width:
(50cm x 50cm, height 100cm) was filled to an empty space of approximately 25%. In the figure, 1 is a septic tank, and 2 is a medium layer in which a catalytic oxidation medium is filled on the slit 3 in the septic tank 1 so that the vacancy is 25%. Further, reference numeral 4 denotes a pipe provided at the upper part of the septic tank 1. When sewage is to be purified, the sewage is introduced through this pipe, and the purified water is discharged through a pipe 6, which will be described later. 5 is an air blowing pipe provided at the bottom of the septic tank 1. Next, 6 is a pipe installed at the bottom of the septic tank 1. When cleaning the sludge adhering to the catalytic oxidation medium 2 with fresh water, clean water is sent from this pipe, and the water used for cleaning is the same as above. Discharge from pipe 4. Next, enter this experimental septic tank 1 from the sewage inlet 4.
Flow rate of 20℃ wastewater containing 30mg BOD/45mg/SS is 0.85~8.5/min (converted to residence time: 4.9~
0.5 hours), and compressed air was blown in from the air inlet 5 at a rate of 20/min.
Purified water was discharged from outlet 6. In this experiment, the wastewater was previously passed through a new oxidation purification medium for 3 hours to allow microorganisms in the wastewater to settle on the medium, and then the wastewater was injected. The results obtained from this experiment are shown in FIGS. 2 and 3. Figures 2 and 3 also show, as comparative examples, crushed granite stones with a diameter of 5 to 40 mm and an apparent specific gravity of 2.53, and cobblestones with a diameter of 5 to 40 mm and an apparent specific gravity of 2.40 in the same experimental septic tank as in Figure 1. was filled to the same vacancy rate as above, and sewage of the same composition was fed in the same manner as above, and compressed air was blown in. The results are also shown. Furthermore, after carrying out the above three types of sewage purification tests for 3 consecutive days, the feeding of sewage was stopped and clean water was fed at a rate of 20/min from the purified water inlet 6, and at the same time, from the air blowing port 5. When compressed air was aerated at a rate of 30/min for 10 minutes and the cleaning water was discharged from outlet 4 for backwashing, the media of the present invention, unlike crushed stone media and cobblestone media, was suspended by the cleaning water and caused mutual frictional movement. The results shown in Table 1 were obtained.
【表】
る。
以上の実験により、本発明の媒体を使用した場
合のBODの除去率は第2図より滞留時間が2時
間程度で95%となること、そしてこの除去率は比
較例として使用した玉石や砕石に比べ1.5倍程度
向上していることが認められた。またSSの除去
率は第3図より汚水の滞留時間が2時間程度でほ
ぼ100%となり、この除去率は比較例に比べて除
去性能が著しく高いことが確認された。そしてま
た、第1表より本発明による媒体に付着した汚泥
の除去率は他の比較例に比べ1.5〜2.3倍高いこと
が認められた。
本発明で使用される水硬性セメントはポルトラ
ンドセメント、高炉セメント、フライアツシユセ
メント、シリカセメント、ジエツトセメントおよ
びアルミナセメント等であつて水硬性セメントは
すべて使用することができる。
本発明の媒体は、水硬性セメントと、特定の骨
材すなわちアライアツシユ、ゼオライト粉粒体及
びALC破砕物の中から選ばれる1種以上の骨材
とを転動造粒して硬化させることにより得られる
表面が粗の球状体であり、径5〜80mmであつて、
見掛比重が1.2〜2.0のものならばすべて使用され
る。本発明の接触酸化浄化媒体の径が5mmよりも
小さいと、汚水の浄化の際に汚泥による閉塞が起
り易いので好ましくなく、また80mmより大きいも
のは転動造粒時に適正な造粒が困難である。そし
てこれら骨材と水硬性セメントとの配合割合は容
積比で水硬化セメント1に対して骨材10以下が望
ましい。なお、本発明において球状体とは球形も
しくは球形に近いものなどをいう。
本発明の媒体を使用して汚水の浄化を行うには
第1図に示したような側面にスリツトのない筒体
を使用することもできるが、底部、側壁に本発明
の媒体を通過せしめぬ程度のスリツトを穿設した
箱体を使用すれば汚水の浄化を一層効果的に行う
ことができる。[Table]
From the above experiments, we found that the BOD removal rate when using the medium of the present invention is 95% when the residence time is about 2 hours as shown in Figure 2, and this removal rate is higher than that of cobblestones and crushed stones used as comparative examples. An improvement of about 1.5 times was observed. Furthermore, as shown in Figure 3, the removal rate of SS reached almost 100% when the residence time of wastewater was about 2 hours, and this removal rate confirmed that the removal performance was significantly higher than that of the comparative example. Furthermore, from Table 1, it was found that the removal rate of sludge adhering to the medium according to the present invention was 1.5 to 2.3 times higher than that of other comparative examples. Hydraulic cements used in the present invention include Portland cement, blast furnace cement, fly ash cement, silica cement, jet cement, and alumina cement, and all hydraulic cements can be used. The medium of the present invention is obtained by rolling granulation and hardening of hydraulic cement and one or more types of aggregate selected from a specific aggregate, ie, Aria Ash, zeolite powder, and crushed ALC. A spherical body with a rough surface and a diameter of 5 to 80 mm,
All materials with an apparent specific gravity of 1.2 to 2.0 are used. If the diameter of the catalytic oxidation purification medium of the present invention is smaller than 5 mm, it is undesirable because clogging with sludge tends to occur during wastewater purification, and if it is larger than 80 mm, proper granulation is difficult during rolling granulation. be. The mixing ratio of these aggregates and hydraulic cement is preferably 10 parts of aggregate to 1 part of hydraulic cement by volume or less. Note that, in the present invention, a spherical body refers to a spherical shape or something close to a spherical shape. In order to purify wastewater using the medium of the present invention, a cylinder without slits on the sides as shown in Fig. 1 can be used; By using a box with slits of approximately 100 to 100 mm, it is possible to purify wastewater even more effectively.
第1図は本発明の媒体を充填する浄化槽の一態
様を示す断面図であり、第2〜3図は本発明の媒
体の実験結果を示すものであつて、このうち第2
図は汚水滞留時間とBOD除去率との関係、第3
図は汚水滞留時間と汚水中のSS除去率との関係
を示す線図である。
図において、1……浄化槽、2……接触酸化媒
体槽、3……スリツト、4……汚水浄化の場合の
汚水送入口または媒体洗浄の場合の洗浄水出口、
FIG. 1 is a cross-sectional view showing one embodiment of a septic tank filled with the medium of the present invention, and FIGS. 2 and 3 show experimental results of the medium of the present invention.
The figure shows the relationship between sewage retention time and BOD removal rate.
The figure is a diagram showing the relationship between wastewater residence time and SS removal rate in wastewater. In the figure, 1... septic tank, 2... contact oxidation medium tank, 3... slit, 4... sewage inlet for sewage purification or wash water outlet for media cleaning,
Claims (1)
ALC破砕物の中から選ばれる1種以上の骨材と
水硬性セメントとを転動造粒して硬化させてな
り、径が5〜80mmの表面が粗の球状体であつて、
見掛比重が1.2〜2.0である汚水の接触酸化浄化媒
体。1 Fly ash, zeolite powder and granules
A spherical body with a rough surface and a diameter of 5 to 80 mm, made by rolling granulating and hardening one or more aggregates selected from crushed ALC and hydraulic cement,
A catalytic oxidation purification medium for wastewater with an apparent specific gravity of 1.2 to 2.0.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57112479A JPS594493A (en) | 1982-07-01 | 1982-07-01 | Medium for cleaning up sewage by contact oxidation |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57112479A JPS594493A (en) | 1982-07-01 | 1982-07-01 | Medium for cleaning up sewage by contact oxidation |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS594493A JPS594493A (en) | 1984-01-11 |
| JPH0155914B2 true JPH0155914B2 (en) | 1989-11-28 |
Family
ID=14587659
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP57112479A Granted JPS594493A (en) | 1982-07-01 | 1982-07-01 | Medium for cleaning up sewage by contact oxidation |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS594493A (en) |
Families Citing this family (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0634993B2 (en) * | 1984-09-17 | 1994-05-11 | 学校法人早稲田大学 | Three-phase fluidized bed water purification method |
| JPS61283436A (en) * | 1985-06-10 | 1986-12-13 | Rotsukii Jiyunkatsu Giken:Kk | Punch for metallic plastic work |
| JPS63115496U (en) * | 1987-01-22 | 1988-07-25 | ||
| WO2009116996A1 (en) | 2008-03-19 | 2009-09-24 | Hewlett-Packard Development Company, L.P. | Computing devices having adjustable keyboard lights |
| CN105565592B (en) * | 2015-12-17 | 2018-12-14 | 江苏泓润生物质能科技有限公司 | A kind of low operating cost countryside sewage treatment equipment |
-
1982
- 1982-07-01 JP JP57112479A patent/JPS594493A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS594493A (en) | 1984-01-11 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US4620931A (en) | Three phase fluidized bed water purifying process | |
| CN106044919B (en) | A kind of method of ammonia nitrogen removal frank in raising river water | |
| KR100413338B1 (en) | Water processing system and processing material of high adsorption | |
| CN105819632B (en) | A method of draining pipe culvert, which is constructed, with zeolite air entrained concrete improves ammonia nitrogen removal frank in draining | |
| CN112661231A (en) | Multifunctional long-acting composite filler and preparation method thereof | |
| JPH0155914B2 (en) | ||
| JP3379924B2 (en) | Adsorbent | |
| JP4947247B2 (en) | Composition for removing nitrate nitrogen and the like and method for producing the same | |
| JP3040097B2 (en) | Contact purification material and method for producing the same | |
| JP2002248498A (en) | Excess sludge treatment method | |
| KR100358888B1 (en) | The multi-pore ceramic using the slag of the by-products from iron-steel-industry and waste casting sand dust and method of making the same | |
| JP2001047086A (en) | Activator for nitric nitrogen denitrification | |
| CN1238275C (en) | Filter material having phosphor adsorbing and biological membrane function and its preparing method | |
| JP3480668B2 (en) | Porous concrete member for water purification for phosphorus removal | |
| CN112830541A (en) | A method for long-term continuous phosphorus removal using multifunctional and long-acting composite fillers | |
| CN114105232A (en) | Silicon steel magnesium oxide wastewater treatment and recycling method | |
| JPH08276198A (en) | River purifying apparatus | |
| JPH022634B2 (en) | ||
| CN111252900A (en) | A kind of lightweight environment-friendly wetland substrate and preparation method thereof | |
| CN110204053A (en) | A kind of efficient dephosphorization Wetland Substrate of wetland engineering and preparation method thereof | |
| KR100506329B1 (en) | Material for water-treating and water-treating apparatus | |
| KR100818547B1 (en) | Tidal Flat Purifying Agent | |
| JPH0550086A (en) | Water treatment contact material | |
| JP2001096271A (en) | Dephosphorizing material for water purification and method for producing the same | |
| JPH08267081A (en) | Microorganisms stuck carrier |