DE2022763A1 - Metal surface treatment bath waste water purification using clay - Google Patents
Metal surface treatment bath waste water purification using clayInfo
- Publication number
- DE2022763A1 DE2022763A1 DE19702022763 DE2022763A DE2022763A1 DE 2022763 A1 DE2022763 A1 DE 2022763A1 DE 19702022763 DE19702022763 DE 19702022763 DE 2022763 A DE2022763 A DE 2022763A DE 2022763 A1 DE2022763 A1 DE 2022763A1
- Authority
- DE
- Germany
- Prior art keywords
- waste water
- clay
- mixture
- baths
- inorganic salt
- 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
- 239000002351 wastewater Substances 0.000 title claims abstract description 31
- 239000004927 clay Substances 0.000 title claims abstract description 12
- 238000004381 surface treatment Methods 0.000 title claims abstract description 9
- 239000002184 metal Substances 0.000 title claims abstract description 8
- 229910052751 metal Inorganic materials 0.000 title claims abstract description 8
- 238000000746 purification Methods 0.000 title 1
- 239000000203 mixture Substances 0.000 claims abstract description 14
- 229910017053 inorganic salt Inorganic materials 0.000 claims abstract description 11
- 238000004062 sedimentation Methods 0.000 claims abstract description 11
- 238000005238 degreasing Methods 0.000 claims abstract description 7
- 239000003995 emulsifying agent Substances 0.000 claims abstract description 3
- 239000003925 fat Substances 0.000 claims abstract description 3
- 239000003960 organic solvent Substances 0.000 claims abstract 2
- 238000000034 method Methods 0.000 claims description 10
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 6
- 229910052742 iron Inorganic materials 0.000 claims description 3
- 240000007594 Oryza sativa Species 0.000 claims description 2
- 235000007164 Oryza sativa Nutrition 0.000 claims description 2
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 claims description 2
- 235000013339 cereals Nutrition 0.000 claims description 2
- 238000004140 cleaning Methods 0.000 claims description 2
- 235000009566 rice Nutrition 0.000 claims description 2
- 230000003311 flocculating effect Effects 0.000 abstract 1
- 229910000360 iron(III) sulfate Inorganic materials 0.000 abstract 1
- 239000002245 particle Substances 0.000 abstract 1
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 9
- 239000012535 impurity Substances 0.000 description 3
- 239000010865 sewage Substances 0.000 description 3
- 241000196324 Embryophyta Species 0.000 description 2
- 238000009713 electroplating Methods 0.000 description 2
- LFMQNMXVVXHZCC-UHFFFAOYSA-N 1,3-benzothiazol-2-yl n,n-diethylcarbamodithioate Chemical compound C1=CC=C2SC(SC(=S)N(CC)CC)=NC2=C1 LFMQNMXVVXHZCC-UHFFFAOYSA-N 0.000 description 1
- NYQDCVLCJXRDSK-UHFFFAOYSA-N Bromofos Chemical compound COP(=S)(OC)OC1=CC(Cl)=C(Br)C=C1Cl NYQDCVLCJXRDSK-UHFFFAOYSA-N 0.000 description 1
- 239000008394 flocculating agent Substances 0.000 description 1
- INLLTDDRGBWXQN-UHFFFAOYSA-H iron(6+) trisulfate Chemical compound S(=O)(=O)([O-])[O-].S(=O)(=O)([O-])[O-].S(=O)(=O)([O-])[O-].[Fe+6] INLLTDDRGBWXQN-UHFFFAOYSA-H 0.000 description 1
- 239000003973 paint Substances 0.000 description 1
- 238000010422 painting Methods 0.000 description 1
- JTJMJGYZQZDUJJ-UHFFFAOYSA-N phencyclidine Chemical class C1CCCCN1C1(C=2C=CC=CC=2)CCCCC1 JTJMJGYZQZDUJJ-UHFFFAOYSA-N 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000000126 substance 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
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- 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
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
-
- 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
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- 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
- C02F1/68—Treatment of water, waste water, or sewage by addition of specified substances, e.g. trace elements, for ameliorating potable water
-
- 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
- C02F2001/007—Processes including a sedimentation step
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/32—Hydrocarbons, e.g. oil
- C02F2101/325—Emulsions
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/16—Nature of the water, waste water, sewage or sludge to be treated from metallurgical processes, i.e. from the production, refining or treatment of metals, e.g. galvanic wastes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/06—Controlling or monitoring parameters in water treatment pH
Landscapes
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
Description
Verfahren zum Reinigen: von Abwässerü der Metalloberflächenbehandlung Die Erfindung betrifft ein Verfahren zum Reinigen von Abwässern der. Metalloberflächenbehandlung. Als solche Abwässer fallen an: einerseits Abwässer. aus Bädern, die organische Lösungs- oder. alkalosche Emulgierungsmittel für Fette enthalten wie Entfettungs- und Phosphatierungsbäder, andererseits Abwässer aus anderen Bädern, z.B. aus Spülbädern von Galvanisier- oder Lackieranlagen. Bisher muss man diese beiden Arten von Abwässern getrennt halten, da man sie nur durch Verfahren: verschiedener Art reinigen: kann. Methods for cleaning up: from waste water to metal surface treatment The invention relates to a method for purifying waste water. Metal surface treatment. Such wastewater occurs: on the one hand, wastewater. from baths containing organic or. contain alkaline emulsifiers for fats such as degreasing and phosphating baths, on the other hand, waste water from other baths, e.g. from rinsing baths from electroplating or Paint shops. So far, these two types of waste water have to be kept separate, since they can only be cleaned by processes of different kinds.
Aufgabe der. Erfindung ist es, ein Verfahren zu entwickeln, durch das ein Abwasser. gereinigt werden kann, das sowohl Abwasser aus Entfettungsbädern als auch Abwässer. aus anderen BE-dern der Metalloberflächenbehandlung enthält.Task of. Invention is to develop a method by that a sewage. can be cleaned, both wastewater from degreasing baths as well as sewage. from other BE countries in metal surface treatment.
Gemäss der Erfindung wird diese Aufgabe dadurch gelöst, dass ein Gemisch aus Entfettungsbäderü und anderen Bädern der Metalloberflächenbehandlung mit Ton von einer Korngrösse unter' 20 mikron und dann ein anorganisches Salz zugesetzt wird, dann dies. Gemisch homogeriiaiert, dann auf. einen pH--Wert von etwa 7 - 9 eingestellt und dann mit einem Sedimentationsbeschleuniger versetzt wird.According to the invention, this object is achieved in that a mixture from degreasing baths and other baths of metal surface treatment with clay with a grain size of less than 20 microns and then an inorganic salt was added will, then this. Mixture homogenized, then on. a pH of around 7 - 9 adjusted and then mixed with a sedimentation accelerator.
Vorzugsweise werden die Abwässer von Bädern der. erstgenannten Art mit Abwässern aus anderen Bädern der. Netalloberflächenbehandlung im Verhältnis von höchstens etwa 1 : 9 gemischt. Falls das Abwasser der. erstgenannten: Art aus Entfettungsbädern Stammt ,. empfiehlt. es: sich, dass das Gemisch auf einen pH-Wert von etwa 8 - 9 eingestellt, dann mit etwa 3 gl Ton versetzt, dann mit etwa 0, 15 - 0, 20 g/S anorga nischem Salz. versetzt, dann im wesentlichen wieder. auf den vorgenannten pH-Wert gebract und dann mit einem Sedimentatlonabes:chleuniger- versetzt wird. Falls: das Abwasser der.Preferably, the wastewater from the baths. first mentioned Art with waste water from other baths in the. Netal surface treatment in proportion mixed at a maximum of about 1: 9. If the wastewater from. former: kind of Degreasing baths. recommends. it: itself that the mixture is at a pH set from about 8 - 9, then added about 3 gl tone, then about 0.15 - 0.20 g / s of inorganic salt. offset, then essentially again. on the aforementioned pH value and then mixed with a Sedimentatlonabes: accelerator will. If: the wastewater from.
erstgenannten Art aus Phosphatierbädern stammt, empfiehlt es sich, dass das Gemisch auf einen: pH-Wert von etwa 7 eingestellt, dann mit etwa 0,25 g/L Ton versetzt, dann mit. etwa 0,1 g/l anorganischem Salz versetzt, dann im wesentlichen wieder: auf den: vorgenannten pH-Wert gebracht und dann mit einem. Sedimentationsbeschleuniger versetzt wird. Als anorganischeß Salz kann insbesondere Eisendreisufat (also Fe2(so4)3) verwendet werden. Zur Abscheidung der: Verunreinigungen empfiehlt sich die Verwendung eines. Absetzzyklons.the first-mentioned type comes from phosphating baths, it is advisable to that the mixture is adjusted to a pH of about 7, then with about 0.25 g / L Sound offset, then with. about 0.1 g / l of inorganic salt are added, then essentially again: brought to the aforementioned pH value and then with a. Sedimentation accelerator is moved. In particular, iron trisulfate (i.e. Fe2 (so4) 3) can be used as an inorganic salt. be used. Use is recommended to separate the: impurities one. Settling cyclones.
Statt Ton kann auch mehr oder. weniger. verunreinigte Tonerde verwendet. werden oder auch Lehm, also verunreinigter Ton, in entsprechend größeren: Mengen. Zum Einstellen des für die Fällung geeigneten pH-Wertes kann z.B. Natronlauge verwendet werden. Als Sedimentationsbeschleuniger (Flockungshilfsmittel) können Stoffe verwendet werden: wie sie zur Zeit unter den Bezeichnungen Sedipur und Praestol auf dem Markt sind; bei den: oben genannten: Abwässerverhältnissen genügt in der Regel eine Menge von etwa 1 mg/l.Instead of sound you can also use more or. fewer. contaminated clay used. or loam, i.e. contaminated clay, in correspondingly larger quantities. Sodium hydroxide, for example, can be used to set the pH value suitable for the precipitation will. Substances can be used as sedimentation accelerators (flocculants) as they are currently on the market under the names Sedipur and Praestol are; In the case of the: above: wastewater conditions, a quantity is usually sufficient of about 1 mg / l.
Beispiele 1. Abwasser eines Entfettungsbades wird mit Reingalvanikabwasser im Verhältnis 1 : 9 gemischt und auf einen pH-Wert von 9 eingestellt.. Diese Mischung wird dann mit 3 g/l Ton versetzt. Danach wird 0,15 g/l Eisendreisulfat zugegeben. Dann wird der pH-Wert durch Zugabe von Natronlauge wieder auf 9 gebracht und dann ein Sedimentationibeschleuniger z.B. 1 mg/l Sedipur TF 5 zugesetzt0 Das auf diese Weise gereinigte Abwasser ist durchsichtig und farblos; seine Restverunreinigungen liegen unterhalb der behördlich vorgeschriebenen Grenze. Examples 1. Waste water from a degreasing bath is mixed with pure electroplating waste water mixed in a ratio of 1: 9 and adjusted to a pH value of 9 .. This mixture 3 g / l clay is then added. Thereafter 0.15 g / l of iron rice sulfate is added. Then the pH is brought back to 9 by adding sodium hydroxide solution and then a sedimentation accelerator e.g. 1 mg / l Sedipur TF 5 added to this Wastewater treated wisely is transparent and colorless; its residual impurities are below the officially prescribed limit.
2. Abwasser. einer Phosphatierungsanlage wird mit Abwasser einer Lackieranlage im Verhältnis 1 : 9 gemischt und auf einen pH-Wert von 7 eingestellt. Diese Mischung wird dann mit 0,25 g/l Ton versetzt. Danach wird 0,1 g/l: Eisen:-dreisulfat zugegeben. Dann wird der pH-Wert durch Zugabe von Natronlauge wieder auf 7 gebrahct und dann. ein /Sedimentationsbeschleuniger zugesetzt. Das auf diese Weise gereinigte Abwasser ist durchsichtig und farblos. Seine Restverunreinigungen liegen unterhalb der behdrdlich vorgeschriebenen Grenze.2. Sewage. a phosphating plant becomes a painting plant with wastewater mixed in a ratio of 1: 9 and adjusted to a pH of 7. This mixture 0.25 g / l clay is then added. Then 0.1 g / l: iron: tri-sulfate is added. Then the pH value is brought back to 7 by adding sodium hydroxide solution and then. a / sedimentation accelerator added. The wastewater treated in this way is transparent and colorless. Its residual impurities are below the official level prescribed limit.
P a t e n t a n s p r ü c h e : P a t e n t a n s p r ü c h e:
Claims (6)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE19702022763 DE2022763A1 (en) | 1970-05-09 | 1970-05-09 | Metal surface treatment bath waste water purification using clay |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE19702022763 DE2022763A1 (en) | 1970-05-09 | 1970-05-09 | Metal surface treatment bath waste water purification using clay |
Publications (1)
Publication Number | Publication Date |
---|---|
DE2022763A1 true DE2022763A1 (en) | 1971-11-18 |
Family
ID=5770695
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
DE19702022763 Pending DE2022763A1 (en) | 1970-05-09 | 1970-05-09 | Metal surface treatment bath waste water purification using clay |
Country Status (1)
Country | Link |
---|---|
DE (1) | DE2022763A1 (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE2526053A1 (en) * | 1975-06-11 | 1977-05-05 | Uetikon Chem Fab | PROCESS FOR THE REMOVAL OF PHOSPHATES FROM AQUATIC SOLUTIONS |
WO2021175891A1 (en) | 2020-03-05 | 2021-09-10 | Atotech Deutschland Gmbh | Purification of metallic objects in the presence of a liquid and layer silicate(s) |
-
1970
- 1970-05-09 DE DE19702022763 patent/DE2022763A1/en active Pending
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE2526053A1 (en) * | 1975-06-11 | 1977-05-05 | Uetikon Chem Fab | PROCESS FOR THE REMOVAL OF PHOSPHATES FROM AQUATIC SOLUTIONS |
WO2021175891A1 (en) | 2020-03-05 | 2021-09-10 | Atotech Deutschland Gmbh | Purification of metallic objects in the presence of a liquid and layer silicate(s) |
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