GB2279070A - Process for the treatment of sewage - Google Patents

Process for the treatment of sewage Download PDF

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Publication number
GB2279070A
GB2279070A GB9411002A GB9411002A GB2279070A GB 2279070 A GB2279070 A GB 2279070A GB 9411002 A GB9411002 A GB 9411002A GB 9411002 A GB9411002 A GB 9411002A GB 2279070 A GB2279070 A GB 2279070A
Authority
GB
United Kingdom
Prior art keywords
glyoxal
sewage
tanks
hydrogen sulphide
aqueous effluent
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.)
Granted
Application number
GB9411002A
Other versions
GB9411002D0 (en
GB2279070B (en
Inventor
Frederic Mabire
Gerard Barbaras
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Sanofi Aventis France
Original Assignee
Francaise Hoechst Ste
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Francaise Hoechst Ste filed Critical Francaise Hoechst Ste
Publication of GB9411002D0 publication Critical patent/GB9411002D0/en
Publication of GB2279070A publication Critical patent/GB2279070A/en
Application granted granted Critical
Publication of GB2279070B publication Critical patent/GB2279070B/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/50Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment

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  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Activated Sludge Processes (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Removal Of Specific Substances (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Treatment Of Sludge (AREA)
  • Treating Waste Gases (AREA)
  • Physical Water Treatments (AREA)

Abstract

Process of the reduction of unpleasant odours normally generated in a sewage plant, said process comprising continously introducing an aqueous solution of glyoxal having a pH of less than 3 into aqueous effluent passing from sedimentation tanks into consolidation tanks in the sewage plant.

Description

PROCESS FOR THE TREATMENT OF SEWAGE The present invention relates to a process for the treatment of sewage in a sewage plant for the purpose of reducing unpleasant odours (olfactory pollution) which emanate from the sewage plant.
The treatment of urban and/or industrial sewage in sewage plants frequently generates foul-smelling gases such as hydrogen sulphide (H2S), which on occasions are even toxic, and which, in the majority of cases, are released in a diluted state into the atmosphere; this creates a serious pollution hazard for personnel and for the waterside environment of these sewage plants.
Moreover, the hydrogen sulphide as well as the various salts and esters dissolved in the waters and sludges during treatment encourages the development of bacteria of the Thiotrix genus which disturbs the efficient operation of the sewage plant by impeding the decantation of sludges.
The treatment of sludges originating from sewage plants with glyoxal absorbed on an inert and water-insoluble mineral solid support such as kieselguhr is known from JP-A-58 (83)-112 098. A process for reducing the concentration of hydrogen sulphide in an aqueous medium containing it, while avoiding the formation of sulphurated derivatives which are insoluble in water, is also known from US-A-4 680 127. This document describes treating the said aqueous medium which has been adjusted to a neutral or alkaline pH beforehand, advantageously to a pH = 9, with an effective quantity of glyoxal, usually in a glyoxal/hydrogen sulphide molar ratio comprised between 1/1 and 2.5/1 and advantageously in a molar ratio of 2.07/1.
Finally, the use of an aqueous solution of glyoxal adjusted to a pH comprised between 5 and 9 for the elimination of odours created by excremental materials and by the products of their treatment, is also known from Japanese Patent Application No. 48-098042. Adjustment of the pH to between 5 and 9 is imperative as aqueous solutions of commercial glyoxal having a pH between 1 and 3 have practically no deodorizing effect, and in addition, they lead to the destruction of microorganisms.
Although the first of the processes described above may avoid the release of hydrogen sulphides by the sludges, it does not resolve the problem caused by the release of hydrogen sulphide from the various water treatment tanks in the sewage plant. As regards the other two processes described above, they require the alkalinization of the water to be treated to a neutral or alkaline pH, which is extremely expensive for a sewage plant treating several thousand cubic metres of water per day.
The present invention provides a process for reducing unpleasant odours in a sewage plant thereby counteracting olfactory pollution which normally occurs, which process comprises introducing an aqueous solution of glyoxal having a pH of less than 3 into a stream of aqueous effluent which passes from sedimentation tanks to consolidation tanks in the said sewage plant.
The process according to the invention is preferably performed by using a commercial aqueous solution of glyoxal, having a pH of less than 3, which is continuously introduced into the aqueous effluents which pass from sedimentation tanks in the sewage plant to so-called consolidation tanks in the sewage plant.
Under further preferred conditions for implementing the invention, the process described above is carried out using: glyoxal in a commercial aqueous solution at 40% by weight, having a pH of about 2; 1 to 24 moles of glyoxal per mole of hydrogen sulphide dissolved in the aqueous effluent to be treated, i.e. 1.7 to 40 g of glyoxal per gram of hydrogen sulphide.
Under even more preferred conditions for implementing the invention, the process described above is carried out using 2.6 + 0.7 moles of glyoxal per mole of hydrogen sulphide dissolved in the aqueous effluent to be treated, i.e. about 4.4 + 1.2 g of glyoxal per gram of hydrogen sulphide.
The process according to the present invention allows on the one hand olfactory pollution of the plant both for the personnel and the waterside environment to be considerably reduced and, on the other hand, the proliferation of filamenteous bacteria of the Thiotrix genus to be avoided without however interfering with the efficient operation of the plant. This last result is surprising as it is known that glyoxal is a powerful bactericide, which is all the more effective when it is used in a pH region below 5.
The present invention will now be illustrated in more detail by the following Example.
EXAMPLE In a sewage plant for urban sewage water treating 24,000 m3/day of sewage, analysis of the air above the consolidation tanks downstream from the sedimentation tanks shows a level of 1,000 vpm (volume per million) of hydrogen sulphide and analysis of the aqueous effluent supplying the consolidation tanks indicates an amount of 21 mg of hydrogen sulphide per litre for a flow of 540 m3/day.
At the start of the process, 0.190 g of a commercial aqueous solution of glyoxal at 40% by weight, having a pH of 2 + 0.5, per litre of aqueous effluent is introduced over a period of 24 hours into the ducts, such as channels or conduits, which supply the said aqueous effluent to the consolidation tanks, i.e. 76 mg (1.31 mmole) of glyoxal, which represents 41 kg (707 moles) of glyoxal, is introduced over a 24 hour period.
At this stage, analysis of the air above the consolidation tanks shows a level of 1 vpm of hydrogen sulphide. The introduction of glyoxal solution (i.e. 0.19 g of a commercial aqueous solution of glyoxal at 40% by weight, having a pH of 2 + 0.5, per litre of aqueous effluent) into the ducts supplying the consolidation tanks is then continued.
After 15 days of treatment, analysis of the air above the consolidation tanks shows a level of less than 1 vpm of hydrogen sulphide. It was also noted that within the plant as a whole, foul-smelling odours no longer existed. In addition, the sludges issuing from the plant, both during their storage and then their distribution, no longer release foul-smelling odours. Moreover, the operation of the plant is not adversely affected by the proliferation of filamentous bacteria of the Thiotrix genus.
This result is obtained, in continuous operation, by a daily consumption of 29.5 mmoles (about 1.71 g) of glyoxal per m3 of sewage arriving at the sewage plant, i.e. a daily consumption of about 102.6 kg of a commercial aqueous solution of glyoxal at 40% by weight, having a pH of 2 + 0.5, for the 3 treatment of 24,000 m3 of sewage.

Claims (4)

1. Process for reducing unpleasant odours in a sewage plant, which process comprises introducing an aqueous solution of glyoxal having a pH of less than 3 into a stream of aqueous effluent which passes from sedimentation tanks to consolidation tanks in the said sewage plant.
2. A process according to claim 1, wherein the amount of glyoxal used is such that 1 to 24 moles of glyoxal are introduced into the said aqueous effluent per mole of hydrogen sulphide present in the said aqueous effluent.
3. A process according to claim 2, wherein the amount of glyoxal used is such that 2.6 + 0.7 moles of glyoxal are introduced into the said aqueous effluent per mole of hydrogen sulphide present in the said aqueous effluent.
4. A process according to claim 1 substantially as described in the foregoing Example.
GB9411002A 1993-06-03 1994-06-02 Process for the treatment of sewage Expired - Fee Related GB2279070B (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
FR9306663A FR2705957B1 (en) 1993-06-03 1993-06-03 Process for treating wastewater in a wastewater treatment plant with a view to eliminating odor nuisances.

Publications (3)

Publication Number Publication Date
GB9411002D0 GB9411002D0 (en) 1994-07-20
GB2279070A true GB2279070A (en) 1994-12-21
GB2279070B GB2279070B (en) 1996-09-25

Family

ID=9447729

Family Applications (1)

Application Number Title Priority Date Filing Date
GB9411002A Expired - Fee Related GB2279070B (en) 1993-06-03 1994-06-02 Process for the treatment of sewage

Country Status (6)

Country Link
BE (1) BE1007195A3 (en)
CH (1) CH687704A5 (en)
ES (1) ES2066740B1 (en)
FR (1) FR2705957B1 (en)
GB (1) GB2279070B (en)
IT (1) IT1265966B1 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7255796B2 (en) 2004-07-08 2007-08-14 General Electric Company Method of preventing hydrogen sulfide odor generation in an aqueous medium

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5343575B2 (en) * 1972-03-30 1978-11-21
JPS6284767A (en) * 1985-10-11 1987-04-18 キャピタル株式会社 Deodorizing liquid
US4680127A (en) * 1985-12-13 1987-07-14 Betz Laboratories, Inc. Method of scavenging hydrogen sulfide
JPH02139083A (en) * 1988-11-18 1990-05-29 Daicel Chem Ind Ltd Process for deodorizing water
DE4002132A1 (en) * 1990-01-25 1991-08-01 Hoechst Ag METHOD FOR trapping SULFUR HYDROGEN WITH GLYOXAL

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
WPI Abstract Accession No 90-206737/27 and JP2139083A *

Also Published As

Publication number Publication date
BE1007195A3 (en) 1995-04-18
FR2705957A1 (en) 1994-12-09
CH687704A5 (en) 1997-01-31
GB9411002D0 (en) 1994-07-20
FR2705957B1 (en) 1995-08-25
ITTO940409A0 (en) 1994-05-20
ES2066740A1 (en) 1995-03-01
ES2066740B1 (en) 1995-11-01
IT1265966B1 (en) 1996-12-16
GB2279070B (en) 1996-09-25
ITTO940409A1 (en) 1995-11-20

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Date Code Title Description
PCNP Patent ceased through non-payment of renewal fee

Effective date: 20080602