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US4370233A Expired / Lapsed US ⏱️ 0.0 years remaining

Chemical detoxification of sewage sludge

Assignee: Cornell Research Foundation Inc
•
Filing: 1981-07-10
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Granted: 1983-01-25
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Expires: 2001-07-10
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Abstract

Abstract A method is disclosed for the chemical detoxification of anaerobically digested organic sludge containing toxic heavy metals in insoluble form. A quantity of the sludge is transferred from a conventional anaerobic digester to an insulated reactor vessel where the sludge is mixed and aerated at a rate sufficient to raise the oxidation reduction potential of the sludge to above +300 mv. and to maintain this condition for a period of 6-12 hours during which the heavy metals are converted to their desired oxidation state. The sludge is then acidified under controlled conditions to pH 1.0-3.0 for a period of 6-12 hours to solubilize the heavy metals. Conventional dewatering techniques are used to separate the detoxified, acidic sludge and the acidic, heavy-metal-containing water. The sludge may be neutralized for safe land application, and the metals can be recovered from the water using existing conventional techniques.

Inventors

  • 👤 Thomas D. Hayes
  • 👤 Randolph M. Kabrick
  • 👤 William J. Jewell

Bibliographic Details

Application Number —
Jurisdiction US
Data Source google_patents
Last Synchronized 2026-11-02 23:27
CPC Classifications
C; C02; C02F; C02F11/00; C02F11/004; C02F1/00; C02F1/72; Y; Y10; Y10S; Y10S210/00; Y10S210/901; Y10S210/902; Y10S210/911; Y10S210/912; Y10S210/918; Y10S210/919

Claims Analysis

Total Claims: 10
Claim 1
Independent Claim 184 words
A method for the chemical detoxification of anaerobically digested organic sludge, which sludge contains toxic heavy metals in insoluble form, comprising the sequential steps of: (a) introducing a quantity of anaerobically digested sludge into an insulated acid-resistant reaction vessel, said sludge having a temperature of from about 30° C. to 60° C.; (b) mixing and aerating said sludge at a rate sufficient to increase the oxidation reduction potential to above +300 mv.; (c) maintaining said increased oxidation reduction potential for a period of 6-12 hours, thereby to convert the heavy metals within the sludge to a desired oxidation state; (d) adding to said sludge a quantity of concentrated acid in an amount sufficient to acidify said sludge to a pH of from about 1.0 to about 3.0 for an acidification period of 6 to 12 hours while maintaining said oxidization reduction potential at a level greater than +300 mv., thereby to convert the oxidized heavy metals to their soluble species; and (e) dewatering the acidified sludge to remove the solubilized heavy metals therefrom, thereby to produce dewatered, detoxified acidic sludge and acidic, heavy-metal-containing water.
Claim 2
Independent Claim 184 words
A method for the chemical detoxification of anaerobically digested organic sludge, which sludge contains toxic heavy metals in insoluble form, comprising the sequential steps of: (a) introducing a quantity of anaerobically digested sludge into an insulated acid-resistant reaction vessel, said sludge having a temperature of from about 30° C. to 60° C.; (b) mixing and aerating said sludge at a rate sufficient to increase the oxidation reduction potential to above +300 mv.; (c) maintaining said increased oxidation reduction potential for a period of 6-12 hours, thereby to convert the heavy metals within the sludge to a desired oxidation state; (d) adding to said sludge a quantity of concentrated acid in an amount sufficient to acidify said sludge to a pH of from about 1.0 to about 3.0 for an acidification period of 6 to 12 hours while maintaining said oxidization reduction potential at a level greater than +300 mv., thereby to convert the oxidized heavy metals to their soluble species; and (e) dewatering the acidified sludge to remove the solubilized heavy metals therefrom, thereby to produce dewatered, detoxified acidic sludge and acidic, heavy-metal-containing water.
Claim 3
Dependent Claim 64 words
The method as recited in claim 1, and further including the step of maintaining said increased oxidation potential by continued aeration of said sludge, said aeration being regulated by an oxidization reduction potential control system including a source of oxygen, and said increased oxidation potential also being maintained by continued mixing of said sludge, thereby achieving uniform distribution of oxygen residuals throughout said sludge.
Claim 4
Dependent Claim 38 words
The method as recited in claim 2, wherein said source of oxygen comprises compressed air, and further wherein said compressed air is introduced into said reactor vessel through spargers evenly spaced at the bottom of said reactor vessel.
Claim 5
Dependent Claim 31 words
The method as recited in claim 1, and further including the step of controlling the addition of said concentrated acid as a function of the pH value of the mixed sludge.
Claim 6
Dependent Claim 40 words
The method as recited in claim 4, wherein said concentrated acid is selected from the group consisting of sulfuric acid and hydrochloric acid, and further wherein the preferred pH value range of said acidified sludge is from 1.5 to 2.5.
Claim 7
Dependent Claim 22 words
The method as recited in claim 1, and further including the step of recovering said heavy metals from said acidic, heavy-metal-containing water.
Claim 8
Dependent Claim 66 words
The method as recited in claim 1, and further including the step of integrating said method into conventional anaerobic municipal sewage treatment systems, wherein a first portion of the sludge stream flowing through said system is directed into said reactor vessel and a second portion of the sludge stream is permitted to bypass said reactor vessel, said second portion being dewatered to produce dewatered more-alkaline sludge.
Claim 9
Dependent Claim 36 words
The method as recited in claim 4, and further including the step of blending said dewatered more-alkaline sludge with said dewatered detoxified acidic sludge, the pH of the resulting mixture being acceptable for direct land application.
Claim 10
Independent Claim 48 words
The method as recited in claims 1 or 8, and further including the step of blending said dewatered detoxified acidic sludge with phosphorous-lime sludges from the tertiary treatment stage of the conventional anaerobic municipal treatment system, the pH of the resulting mixture being acceptable for direct land application.

References Cited (Backward Citations)

US3649534A Cited
US3864247A Cited
US3838198A Cited
US3961078A Cited
US3892660A Cited
US4000064A Cited
FR2327965A1 Cited
US4159944A Cited
US4277342A Cited

USPTO Annuity & Maintenance Windows

Annuity Stage Window Opens Payment Deadline Surcharge Period Until Estimated Fee Status
3.5 Years (Year 4) 1986-01-24 1986-07-26 1987-01-25 $2000.00 Window Closed / Lapsed
7.5 Years (Year 8) 1990-01-24 1990-07-26 1991-01-25 $3760.00 Window Closed / Lapsed
11.5 Years (Year 12) 1994-01-24 1994-07-26 1995-01-25 $7700.00 Window Closed / Lapsed

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