IP Library Granted Patent US 7,887,706
Granted Patent B2
US 7,887,706 · App. 12/415,166 · Granted Feb 15, 2011

Method of biofiltration of a liquid effluent

View Patent ↗
Loading inventors, assignments & file history…
Monitor This Case
Get email alerts when status or documents change.
Order Certified Copies
Most orders are placed with the USPTO same day — all within 24 business hours.
Order via The Patent Place →
Pre-filled with this patent's details
Quick Facts
Patent No.
US 7,887,706
App. No.
12/415,166
Granted
Feb 15, 2011
Kind
B2
Abstract

A method of biofiltration of a liquid effluent by simultaneous nitrification and denitrification uses the adding of an oxygen source at a predetermined rate and optionally the adding of a carbon source (such as whey) thus enabling the complete transformation of the nitrates (NO 3 ) present in the effluent at the time of treatment through a biofilter. The specific operating conditions favoring the simultaneous nitrification and denitrification include the controlled injection of a slight quantity of air, adjustment of the level of nitrogen load (TKN+NO 3 ) and the level of carbon load thereby making possible elimination for the most part of the release of unwanted nitrogen in the form of NO 3 or NO 2 .

Claims (35)

1. A method for purifying a liquid effluent containing ammoniacal nitrogen, with or without nitrates, by simultaneous nitrification and denitrification, said method comprising the adding of oxygen with a flow rate varying from 0.1 to 0.66 m 3 /m 2 .hour to a trickling biofilter in order to recuperate a substantially purified effluent at an outlet of the biofilter.

2. A method according to claim 1 , comprising the following steps:

i) feeding the liquid effluent to be purified to an entrance of the biofilter at a level of nitrogen load varying between 0.01 and 0.04 kg TKN/m 2 .day and a carbon load varying between 0.05 and 0.15 kg BOD 5 /m 2 .day;

ii) performing said oxygen addition according to said flow rate; and

iii) recuperating a substantially purified effluent at the outlet of the biofilter.

3. The method according to claim 1 , to purify a liquid effluent containing ammoniacal nitrogen, with or without nitrates, wherein said trickling biofilter is provided with a filtering medium supporting microorganisms capable of lowering the content of ammoniacal nitrogen of the liquid effluent in the presence of oxygen, and microorganisms capable of denitrifying the liquid effluent under substantially anoxic conditions.

4. The method according to claim 1 , comprising the following steps:

i) feeding the liquid effluent being purified to an entrance of the biofilter while adjusting the nitrogen load between 0.01 and 0.04 kg TKN/m 2 .day;

I′) optionally, adding to the effluent a carbon source at a predetermined load depending on the quantity of TKN initially contained in the effluent;

ii) performing said oxygen addition according to said flow rate; and

iii) recuperating a substantially purified effluent at the outlet of the biofilter.

5. A method according to claim 1 , comprising the following steps:

i) feeding the liquid effluent being purified to an entrance of the biofilter while adjusting the overall nitrogen load between 0.01 and 0.055 kg TKN+NO 3 /m 2 .day;

I′) optionally, adding to the effluent a carbon source at a predetermined dosage depending on the overall quantity of nitrogen (TKN+NO 3 ) initially contained in the effluent;

I″) letting the effluent trickle through the filtering medium in contact with the carbon source to promote the denitrification of the effluent;

ii) performing said oxygen addition to the effluent treated at step ii′) according to said flow rate;

ii′) letting the effluent trickle through the filtering medium in contact with the oxygen to lower the content of ammoniacal nitrogen in the effluent; and

iii) recuperating a substantially purified liquid effluent at the outlet of the biofilter.

6. The method according to claim 1 , wherein the effluent substantially purified contains between 0 and 200 mg/L of nitrogen in the form of N—NO 2 and N—NO 3 .

7. The method according to claim 6 , wherein the effluent substantially purified contains between 0 and 150 mg/L of nitrogen in the form of N—NO 2 and N—NO 3 .

8. The method according to claim 7 , wherein the effluent substantially purified contains less than 100 mg/L of nitrogen in the form of N—NO 2 and N—NO 3 .

9. The method according to claim 1 , wherein the effluent substantially purified contains between 0 and 200 mg/L of TKN.

10. The method according to claim 9 , wherein the effluent substantially purified contains between 0 and 150 mg/L of TKN.

11. The method according to claim 10 , wherein the effluent substantially purified contains less than 100 mg/L of TKN.

12. The method according to claim 1 , wherein the oxygen is furnished in the form of: pure oxygen or a gas containing oxygen.

13. The method according to claim 12 , wherein the oxygen is furnished in the form of air at a rate varying between 0.5 and 3.3 m 3 /m 2 .hour.

14. The method according to claim 2 , wherein the nitrogen load level at step i) varies between 0.015 and 0.035 kg TKN/m 2 .day; the load level of carbon source at step i) varies between 0.08 and 0.15 kg BOD 5 /m 2 .day; and the oxygen source is in the form of air and the aeration rate at step ii) varies between 1.0 and 3.0 m 3 /m 2 .hour.

15. The method according to claim 14 , wherein the nitrogen load level at step i) varies between 0.02 and 0.035 kg TKN/m 2 .day; the load level of carbon source at step i) varies between 0.08 and 0.12 kg BOD 5 /m 2 .day; and the aeration rate at step ii) varies between 1.5 and 3.0 m 3 /m 2 .hour.

16. The method according to claim 15 , wherein the nitrogen load level at step i) is set at about 0.029 kg TKN/m 2 .day; the load level of carbon source at step i) is set at about 0.1 kg BOD 5 /m 2 .day; and the aeration rate at step ii) is set at about 2.5 m 3 /m 2 .hour.

17. The method according to claim 1 , wherein the filtration rate is between 0.01 and 0.3 m 3 /m 2 .day.

18. The method according to claim 1 , wherein the aeration is continuous or intermittent.

19. The method according to claim 3 , wherein the filtering medium is at least one element selected from the group consisting of: pozzolana; peat; wood chips; gravel; and calcite.

20. The method according to claim 1 , wherein said liquid effluent containing ammoniacal nitrogen, with or without nitrates, is liquid manure.

21. The method according to claim 20 , wherein said manure comes from the swine industry.

22. The method according to one of claims 4 or 5 , wherein the source of carbon load is selected from the group consisting of: whey, methanol, glucose or a liquid manure coming from the farming industry.

Assignments (3)
ASSIGNMENT OF ASSIGNOR'S INTEREST Recorded Jun 18, 2009
From: LESSARD, PAUL
To: UNIVERSITE LAVAL
Reel/Frame 022841/0092 →
ASSIGNMENT OF ASSIGNOR'S INTEREST Recorded Jun 18, 2009
From: UNIVERSITE LAVAL
To: CENTRE DE RECHERCHE INDUSTRIELLE DU QUEBEC
Reel/Frame 022843/0639 →
ASSIGNMENT OF ASSIGNOR'S INTEREST Recorded Jun 17, 2009
From: BUELNA, GERARDO; LE BIHAN, YANN; DUBE, RINO; DUFOUR-L'ARRIVEE, CAROLINE
To: CENTRE DE RECHERCHE INDUSTRIELLE DU QUEBEC
Reel/Frame 022837/0681 →
Priority Claims (1)
CA 2626911 · Mar 31, 2008 · national
Continuity (2)
Provisional Application 61161602 · Mar 19, 2009
Related Publication 20090242482A1 · Oct 1, 2009