DE2211890A1 - Waste water purification - using conc hydrogen peroxide forming nascent oxygen recombined for biological purification - Google Patents
Waste water purification - using conc hydrogen peroxide forming nascent oxygen recombined for biological purificationInfo
- Publication number
- DE2211890A1 DE2211890A1 DE2211890A DE2211890A DE2211890A1 DE 2211890 A1 DE2211890 A1 DE 2211890A1 DE 2211890 A DE2211890 A DE 2211890A DE 2211890 A DE2211890 A DE 2211890A DE 2211890 A1 DE2211890 A1 DE 2211890A1
- Authority
- DE
- Germany
- Prior art keywords
- oxygen
- waste water
- hydrogen peroxide
- decomposed
- biological
- 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
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 title claims abstract description 28
- 239000002351 wastewater Substances 0.000 title claims abstract description 18
- 238000000746 purification Methods 0.000 title claims abstract description 7
- 229910052760 oxygen Inorganic materials 0.000 title claims description 19
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 title claims description 18
- 239000001301 oxygen Substances 0.000 title claims description 18
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 12
- 239000000126 substance Substances 0.000 claims abstract description 9
- 239000003054 catalyst Substances 0.000 claims abstract description 6
- 239000013543 active substance Substances 0.000 claims abstract 2
- 238000005352 clarification Methods 0.000 claims abstract 2
- 229910001385 heavy metal Inorganic materials 0.000 claims abstract 2
- 238000000034 method Methods 0.000 claims description 7
- 230000006798 recombination Effects 0.000 claims description 2
- 238000005215 recombination Methods 0.000 claims description 2
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 claims 1
- 229910001882 dioxygen Inorganic materials 0.000 claims 1
- 239000000463 material Substances 0.000 abstract description 3
- 239000010802 sludge Substances 0.000 description 5
- 238000004140 cleaning Methods 0.000 description 4
- 238000000354 decomposition reaction Methods 0.000 description 4
- 239000010865 sewage Substances 0.000 description 3
- 244000005700 microbiome Species 0.000 description 2
- 230000001590 oxidative effect Effects 0.000 description 2
- 150000002989 phenols Chemical class 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- ISPYQTSUDJAMAB-UHFFFAOYSA-N 2-chlorophenol Chemical group OC1=CC=CC=C1Cl ISPYQTSUDJAMAB-UHFFFAOYSA-N 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- NHYCGSASNAIGLD-UHFFFAOYSA-N Chlorine monoxide Chemical class Cl[O] NHYCGSASNAIGLD-UHFFFAOYSA-N 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- 241000270295 Serpentes Species 0.000 description 1
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 description 1
- OUUQCZGPVNCOIJ-UHFFFAOYSA-M Superoxide Chemical compound [O-][O] OUUQCZGPVNCOIJ-UHFFFAOYSA-M 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 235000011116 calcium hydroxide Nutrition 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 150000001720 carbohydrates Chemical class 0.000 description 1
- 235000014633 carbohydrates Nutrition 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 239000003599 detergent Substances 0.000 description 1
- YADSGOSSYOOKMP-UHFFFAOYSA-N dioxolead Chemical compound O=[Pb]=O YADSGOSSYOOKMP-UHFFFAOYSA-N 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 230000000977 initiatory effect Effects 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 238000009372 pisciculture Methods 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 239000008213 purified water Substances 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
- 239000003643 water by type Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/025—Biological purification using sources of oxygen other than air, oxygen or ozone
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/722—Oxidation by peroxides
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
- C12N1/38—Chemical stimulation of growth or activity by addition of chemical compounds which are not essential growth factors; Stimulation of growth by removal of a chemical compound
-
- 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
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Microbiology (AREA)
- Water Supply & Treatment (AREA)
- Biodiversity & Conservation Biology (AREA)
- Environmental & Geological Engineering (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Hydrology & Water Resources (AREA)
- Genetics & Genomics (AREA)
- Biotechnology (AREA)
- Wood Science & Technology (AREA)
- Zoology (AREA)
- Biochemistry (AREA)
- General Engineering & Computer Science (AREA)
- General Health & Medical Sciences (AREA)
- General Chemical & Material Sciences (AREA)
- Biomedical Technology (AREA)
- Virology (AREA)
- Medicinal Chemistry (AREA)
- Tropical Medicine & Parasitology (AREA)
- Molecular Biology (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
- Activated Sludge Processes (AREA)
- Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
Abstract
Description
J2rfailrn 7i' Reinigung von Abwasser Die zunehmende Verschmutzung der Flusse- und Seen durch nicht genügend geklärte Abwässer macht es erforderlich, daß Verfahren angewendet werden, die bei relativ geringem Platzbedarf in der Lage sind, insbesondere industrielle Verunreinigungen auf kleinem Raum unschädlich zu machen. In den Abwässern befinden sich normalel eise a) ungelöste Stoffe anorganischer und organischer Natur und b) gelöste Stoffe beider Arten. J2rfailrn 7i 'Purification of Sewage Increasing Pollution of rivers and lakes due to insufficiently treated sewage makes it necessary that methods are used that are capable of using a relatively small amount of space are harmless, especially industrial contamination in a small space do. Normally there are a) undissolved inorganic substances in the wastewater and organic in nature and b) solutes of both types.
Die Entfernung der ungelösten Stoffe wird im allgemeinen mechanisch durch Sandfänger, Absetzbecken, Klärtrichter und Spülsiebe bewirkt, während die spezifisch leichteren Schwebstoffe durch diese Methode nicht entfernt werden können. Durch Zusatz von chemischen Klärmitteln wie z. B. Kalkmilch oder Aluminiumsulfat wird die Sedimentatiun dieser Schwebstoffe zwar beschleuniyt, jedoch fallen bei diesem Verfahren sehr große Schlammengen an AuRerdem können diese Zusätze den Vorfluter schädigen. Die organischen Verunreinigungen bedeuten durch ihre Sauerstoffzehrung im Vorfluter eine Gefahr für die Fischzucht. Sind stickstoffhaltige Verbindungen und Kohlehydrate im Abwasser, so können stinkende Fäulnis und sekundäre Fäulnis auftreten. Bei der biologischen Reinigung erfolgt die Zerstörung der organischen Substanz durch Mikroorganismen in Gegenwart von Sauerstoff. Es-hat sich nun gezeigt, daß, insbesondere durch die zunehmende Verwendung von Detergentien, durch einfaches Einblasen von Luft oder auch von Sauerstoff die erforderliche Anreicherung des Abwassers mit Sauerstoff nicht oder nur unvollständig erreicht werden kann.The removal of the undissolved matter is generally mechanical caused by sand traps, settling basins, septic tanks and rinsing strainers, while the specifically lighter suspended solids cannot be removed by this method. By adding chemical clarifiers such. B. milk of lime or aluminum sulfate the sedimentation of these suspended solids is accelerated, but they fall In addition, these additives can destroy the receiving water damage. The organic impurities mean by their consumption of oxygen a danger to fish farming in the receiving waters. Are nitrogenous compounds and carbohydrates in sewage, so can smelly putrefaction and secondary putrefaction appear. In the case of biological cleaning, the organic ones are destroyed Substance produced by microorganisms in the presence of oxygen. It has now been shown that, especially due to the increasing use of detergents, by simple Blowing in air or oxygen, the necessary enrichment of the wastewater with oxygen cannot be reached or only incompletely.
Aufgabe der vorliegenden Erfindung ist es, eine Anreicherung des Abwassers mit Sauerstoff zu bewirken, wobei getrennt wird nach einmal der oxydierenden Wirkung des Sauerstoffs im status nascendi in jenem Bereiche des Abwassers, in dem die bioligisc,he Reinigung infolge der Anvesenheit von die Organismen schädigenden Stoffen nicht möglich ist, und im weiteren durch Anreicherung mit nicht mehr nascierendem Sauerstoff in Jenem Teil der Anlage, der zur biologischen Reinigung bestimmt ist.The object of the present invention is to enrich the wastewater to effect with oxygen, being separated after once the oxidizing effect of oxygen in the status nascendi in that area of the wastewater in which the bioligisc, he No cleaning due to the presence of substances harmful to organisms is possible, and in the further by enrichment with no longer nasal Oxygen in that part of the system that is intended for biological cleaning.
Es ist bekannt, dan man die oxydierende irlrung von Chloroxyden auch zur Abwasserreinigung anwendet. Dieses Verfahren ist jedoch unzulässig, wenn das Abwasser Phenole enthält, da das frei werdende Chlor mit den Phenolen Chlorphenol bildet, das das gereinigte Wasser ungenießbar werden läßt. Dieer Nachteil wird bei Verwendung von hochkonzentriertem Wasserstoffsuperoxyd vermieden.It is known that the oxidizing process of chloroxides is also known used for wastewater treatment. However, this procedure is not permitted if that Wastewater contains phenols, as the chlorine released with the phenols is chlorophenol forms, which makes the purified water inedible. The disadvantage is with Avoid using highly concentrated hydrogen peroxide.
Die Anwendung des nascierenden Sauerstoffs erfolgt zweckmäBig in einer geschlossenen Anlage, in der das zu behandelnde, schon durch mechanische Mittel eingedickte Abwasser mit hohem Schlanmenteil durch Rührer etc. in Bewegung gehalten wird. Das hochkonzentrierte Wasserstoffsuperoxyd wird entweder durch poröse, keramische Platten direkt in dieses Gefäß eingeleitet, wobei eine Feinverteilung des austretenden Wasserstoffsuperoxyds durch die Struktur der Poren gewährleistet wird, oder es wird durch ein Katalysatorbett, das in unmittelbarem Kontakt mit dem Abwasser steht, gedrückt und katalytisch zersetzt. Im ersten Falle ist für die Zersetzung des Mittals die Anwesenheit von katalytisch oder chemisch auf das Wasserstoffsupsroxyd einwirkenden Substanzen am Schlamm Voraussetzung, z. B. Schwer-talle, während im zweiten Falle das Abwasser frei von solchen Stoffen sein kann. In beiden Fällen entsteht unmittelbar im Bereich des Schlammes nascierender Sauerstoff neben Wasser.The application of the nascent oxygen is expediently carried out in one closed plant in which the to be treated, already by mechanical means Thickened wastewater with a high part of the snake kept in motion by stirrers etc. will. The highly concentrated hydrogen peroxide is either porous, ceramic Plates introduced directly into this vessel, with a fine distribution of the emerging Hydrogen peroxide is ensured by the structure of the pores, or it becomes through a catalyst bed that is in direct contact with the wastewater, pressed and catalytically decomposed. The first case is for the decomposition of the Mittal the presence of catalytically or chemically acting on the hydrogen hydroxide Substances on the sludge prerequisite, e.g. B. heavy tales, while in the second case the wastewater can be free of such substances. In both cases arises immediately nascent oxygen next to water in the area of the mud.
Die frei werdende Zersetzungswärme des Wasserstoffsuperoxyds beschleunigt die Oxydationsvorgänge. Die Menge des zu zersetzenden Wosssrstoffsupsroxyds und die Verweilzeit des Abwassers im geschlossenen System sind abhängig von der Art des Schlammes, der oxydiert werden soll. Durch bekannte apparative Mittel kann diese Zeit exakt bestimmt werden. Zweckmäßig wird das Wasserstoffsuperoxyd in Konzentrationen von 80 bis 85 46 angewendet. Das Einbringen in das geschlossene Gefäß kann entweder durch den statischen Druck der Wasserstoffsuperoxyd-Sdule bei hochgelegenen Behälter geschehen oder mit Hilfe von Dosierpumpen durchgeführt werden. Behälter und Rohrleltungen, die mit dem Wasserstoffsuperoxyd in Kontakt kommen, müssen aus Reinalu bestehen oder durch-geeignete Kunststoffüberw züge gegen den Angriff des Mittels geschützt sein.The heat of decomposition released by the hydrogen peroxide accelerates the processes of oxidation. The amount of hydrogen sulfide to be decomposed and the residence time of the wastewater in the closed system depends on the type of the sludge to be oxidized. This can be done by known apparatus Time can be determined exactly. The hydrogen peroxide is expedient in concentrations from 80 to 85 46 applied. The introduction into the closed vessel can either due to the static pressure of the hydrogen peroxide column when the container is at a high level happen or be carried out with the help of metering pumps. Containers and pipelines, that come into contact with the hydrogen peroxide, must from Reinalu exist or by-suitable plastic covers against the attack of the agent be protected.
Zweckmäßig erscheint auch folgende Ausbildung des Einleitvorganges : Die den Schlamm umwälzenden Rührflügel enthalten Kanäle, die mit der das Wassarstoffauperoxyd zuführenden Hohlwelle in Verbindung stehen. Diese Kanäle sind einseitig zum Gefäß zu mit z. B. porösem, keromischem Material abgedeckt, durch das das Wasserstoffsupperoxyd ausgepreßt wird. Eine derartige Vorrichtung wird eine optimale Vermischung von Schlamm und Wasserstoffsuperoxtyd garantieren.The following formation of the initiation process also appears expedient : The agitator blades that circulate the sludge contain channels that connect with that of the Wassarstoffauperoxyd feeding hollow shaft are in connection. These channels are one-sided to the vessel to with z. B. porous, keromic material covered through which the hydrogen superoxide is squeezed. Such a device will provide optimal mixing of sludge and hydrogen peroxide guarantee.
Bei Verwendung eines Katalysatorbettes zur Zersetzung des Wasssrstoffsuperoxydes, wenn also im Schlamm die die Zersetzung bewirkenden Substanzen fehlen, sind ein Siebsystem aus Silberdraht oder Sleiplatten mit einem Überzug von Bleisuperoxyd brauchber. Diese Betten können direkt in die Zuleitungsrchre unmittelbar vor Eintritt in das Gefäß eingesetzt werden.When using a catalyst bed to decompose the hydrogen peroxide, So if the substances causing the decomposition are missing in the sludge, a Sieve system made of silver wire or Sleiplatten with a coating of lead peroxide need. These beds can be placed directly in the supply duct immediately before entry be inserted into the vessel.
Zur Anreicherung das Abwassers lit Sauerstoff für die biologische Reinigung darf dieser nicht im status nascendi vorliegen, da er in di@@@@ Falle die Mikroorgenismen schädigen wörde.To enrich the wastewater lit oxygen for the biological Cleaning, this must not be in the status nascendi, as it is in the case of di @@@@ which would damage the microorganisms.
Aus dies@@ Grunde @uß die Zersetrung des Wasserstoffsuperoxyds @ußerhalb des Vorfluters erfolgen. Zwischen Zer@etzer und Eintritt des mit Bauurutoff angereicherten Wassers in den Vorfluter wird eine Rohrstr@cke @eschaltet, deren Länge so bemassen ist, daß in Abhängigkeit von der Btrömungsgeschwindigkeit des Wasser/Sauerstoffgemisches eine Rekombination des nascierenden Sausratoffa zum nornal@n, mol@kuleren Sauerstoff @rfolgen kann.This is the reason for the decomposition of the hydrogen peroxide outside of the receiving water. Between Zer @ etzer and entry of the enriched with Bauurutoff Water in the receiving water, a pipe line is switched, the length of which is measured is that depending on the flow rate of the water / oxygen mixture a recombination of the nascent Sausratoffa to normal @ n, mol @ kuleren oxygen @ can be done.
Claims (2)
Priority Applications (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| DE2211890A DE2211890A1 (en) | 1972-03-11 | 1972-03-11 | Waste water purification - using conc hydrogen peroxide forming nascent oxygen recombined for biological purification |
| DE19722236504 DE2236504B2 (en) | 1972-03-11 | 1972-07-13 | PROCESS FOR MEETING OXYGEN REQUIREMENTS IN AEROBIC WASTE WATER PURIFICATION AND TECHNICAL MICROBIOLOGY |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| DE2211890A DE2211890A1 (en) | 1972-03-11 | 1972-03-11 | Waste water purification - using conc hydrogen peroxide forming nascent oxygen recombined for biological purification |
| DE19722236504 DE2236504B2 (en) | 1972-03-11 | 1972-07-13 | PROCESS FOR MEETING OXYGEN REQUIREMENTS IN AEROBIC WASTE WATER PURIFICATION AND TECHNICAL MICROBIOLOGY |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| DE2211890A1 true DE2211890A1 (en) | 1973-09-20 |
Family
ID=32714339
Family Applications (2)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| DE2211890A Pending DE2211890A1 (en) | 1972-03-11 | 1972-03-11 | Waste water purification - using conc hydrogen peroxide forming nascent oxygen recombined for biological purification |
| DE19722236504 Withdrawn DE2236504B2 (en) | 1972-03-11 | 1972-07-13 | PROCESS FOR MEETING OXYGEN REQUIREMENTS IN AEROBIC WASTE WATER PURIFICATION AND TECHNICAL MICROBIOLOGY |
Family Applications After (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| DE19722236504 Withdrawn DE2236504B2 (en) | 1972-03-11 | 1972-07-13 | PROCESS FOR MEETING OXYGEN REQUIREMENTS IN AEROBIC WASTE WATER PURIFICATION AND TECHNICAL MICROBIOLOGY |
Country Status (1)
| Country | Link |
|---|---|
| DE (2) | DE2211890A1 (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP0008074A1 (en) * | 1978-08-12 | 1980-02-20 | Bayer Ag | Process for the chemical and biological treatment of waste water |
| FR2493824A1 (en) * | 1980-11-08 | 1982-05-14 | Akzo Nv | DEVICE FOR ENRICHING OXYGEN LIQUIDS |
| DE4119144A1 (en) * | 1991-06-11 | 1992-12-17 | Weidner & Co Kg | Biological, chemical and physical processing of contaminated water - involves pre-treatment with oxidising agents including hydrogen peroxide and catalysts |
Families Citing this family (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE2530722C2 (en) * | 1975-07-10 | 1984-05-24 | Wolf-Rüdiger Dipl.-Ing. 7000 Stuttgart Müller | Process for nitrification, demanganization and iron removal from contaminated water |
| DE2608899C3 (en) * | 1976-03-04 | 1982-12-30 | Müller, Wolf-Rüdiger, Dipl.-Ing., 7000 Stuttgart | Process to improve the backwashing process for filters made of granular materials through the use of hydrogen peroxide (H ↓ 2 ↓ O ↓ 2 ↓) |
| DE3011247C2 (en) * | 1980-03-24 | 1982-10-28 | Schreiber-Kläranlagen Dr.-Ing. Aug. Schreiber GmbH & Co KG, 3012 Langenhagen | Process for cleaning waste water using activated sludge |
| DE3017289C2 (en) * | 1980-05-06 | 1984-11-22 | Rudolf 8551 Adelsdorf Messner | Device for the biological purification of waste water |
| DE3543408A1 (en) * | 1985-12-07 | 1987-06-11 | Schreiber Berthold | Process for sewage purification using activated sludge |
| DE3703824A1 (en) * | 1987-02-07 | 1988-08-18 | Thomae Gmbh Dr K | METHOD FOR SIMULTANEOUSLY CHEMICAL AND BIOLOGICAL DISPOSAL OF SOLID AND LIQUID ORGANIC WASTE AND DEVICES FOR CARRYING OUT THIS METHOD |
-
1972
- 1972-03-11 DE DE2211890A patent/DE2211890A1/en active Pending
- 1972-07-13 DE DE19722236504 patent/DE2236504B2/en not_active Withdrawn
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP0008074A1 (en) * | 1978-08-12 | 1980-02-20 | Bayer Ag | Process for the chemical and biological treatment of waste water |
| US4549969A (en) * | 1980-08-11 | 1985-10-29 | Akzo Nv | Process and an apparatus for enriching liquids with oxygen |
| FR2493824A1 (en) * | 1980-11-08 | 1982-05-14 | Akzo Nv | DEVICE FOR ENRICHING OXYGEN LIQUIDS |
| US4440648A (en) * | 1980-11-08 | 1984-04-03 | Akzo Nv | Process and an apparatus for enriching liquids with oxygen |
| DE4119144A1 (en) * | 1991-06-11 | 1992-12-17 | Weidner & Co Kg | Biological, chemical and physical processing of contaminated water - involves pre-treatment with oxidising agents including hydrogen peroxide and catalysts |
Also Published As
| Publication number | Publication date |
|---|---|
| DE2236504A1 (en) | 1974-01-31 |
| DE2236504B2 (en) | 1977-12-15 |
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