IP Library Patent Application 15305603
Patent Application
App. No. 15/305,603

REMOVAL OF SELENOCYANATE FROM REFINERY SOUR WATER STRIPPER WASTEWATER

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Patent No.
US None
App. No.
15/305,603
Abstract

Systems and methods for removing heavy metals such as selenium from wastewater with zero valent iron media. Air may be introduced directly into a reaction zone of a fluidized bed reactor filled with the media to catalyze treatment.

Claims (43)

1 . A system for the removal of selenium from sour water stripper wastewater, the system comprising:

a fluidized bed reactor including:

a reactor body;

a mixer disposed in a lower portion of the reactor body;

a reaction zone defined about the mixer; and

an air supply configured to inject air directly into the reaction zone.

2 . The system of claim 1 , wherein the reaction zone is located in a lower portion of the fluidized bed reactor.

3 . The system of claim 2 , wherein the fluidized bed reactor further comprises a chimney disposed within the reactor body, and the reaction zone is defined below the chimney.

4 . The system of claim 1 , comprising a plurality of fluidized bed reactors fluidly connected in series.

5 . The system of claim 1 , wherein the fluidized bed reactor includes zero-valent iron media.

6 . The system of claim 5 , wherein the zero-valent iron media is coated with an iron oxide.

7 . The system of claim 6 , wherein the zero-valent iron media is coated with magnetite.

8 . The system of claim 1 , further comprising a source of Fe 2+ ions in fluid communication with fluidized bed reactor.

9 . The system of claim 1 , further comprising a source of a pH adjustment agent in fluid communication with fluidized bed reactor.

10 . The system of claim 1 , further comprising an aeration basin in fluid communication downstream of the fluidized bed reactor.

11 . The system of claim 10 , further comprising a source of pH adjuster in fluid communication with the aeration basin.

12 . The system of claim 10 , further comprising a solids/liquid separator in fluid communication downstream of the aeration basin.

13 . The system of claim 12 , wherein the solids/liquid separator is configured to produce a supernatant and settled sludge and to direct at least a portion of the settled sludge into the fluidized bed reactor.

14 . The system of claim 1 , further comprising an equalization vessel in fluid communication upstream of the fluidized bed reactor.

15 . The system of claim 14 , wherein the equalization vessel includes a sour water stripper wastewater inlet in fluid communication with a source of sour water stripper wastewater.

16 . The system of claim 14 , further comprising a source of pH adjuster in fluid communication with the equalization vessel.

17 . The system of claim 14 , further comprising a source of oxidizer in fluid communication with the equalization vessel.

18 . The system of claim 1 , further comprising an oxidation vessel in fluid communication downstream of the fluidized bed reactor.

19 . The system of claim 1 , further comprising a flocculation vessel in fluid communication downstream of the fluidized bed reactor.

20 . The system of claim 1 , wherein the air supply is configured to inject the air into the reaction zone above the mixer.

21 . The system of claim 1 , wherein the air supply is configured to inject the air into the reaction zone below the mixer.

22 . The system of claim 1 , wherein the air supply is configured to inject the air into the reaction zone at substantially a same depth as the mixer.

23 . A method of removing heavy metals from wastewater, the method comprising:

directing the wastewater into a fluidized bed reactor including a zero-valent iron media;

mechanically mixing the wastewater in the fluidized bed reactor with a mixer to contact contaminants in the wastewater with the zero-valent iron media; and

injecting an oxygen containing gas into a reaction zone defined about the mixer.

24 . The method of claim 23 , wherein injecting the oxygen containing gas into the reaction zone includes injecting the oxygen containing gas into a lower portion of the fluidized bed reactor.

25 . The method of claim 24 , wherein the wastewater includes selenium and the method includes removing approximately 75% or more of the selenium from the wastewater in a single pass through a system including the fluidized bed reactor.

26 . The method of claim 25 , wherein the method includes removing approximately 99% or more of the selenium from the wastewater in a single pass through a system including the fluidized bed reactor.

27 . The method of claim 23 , wherein the wastewater includes selenium and the method includes reducing a concentration of selenium in the wastewater to below 50 ppb in a single pass through a system including the fluidized bed reactor.

28 . The method of claim 23 , wherein the wastewater includes selenium and the method includes reducing a concentration of selenium in the wastewater from above 400 ppb to below 5 ppb in a single pass through a system including the fluidized bed reactor.

29 . The method of claim 23 , wherein directing the wastewater into the fluidized bed reactor including the zero valent iron media includes directing the wastewater into a fluidized bed reactor including zero valent iron media coated with magnetite.

30 . The method of claim 29 , further comprising adding a source of Fe 2+ ions into the fluidized bed reactor.

31 . The method of claim 30 , wherein the source of Fe 2+ ions is added to the fluidized bed reactor at a flow rate that maintains the concentration of Fe 2+ ions in the wastewater coming into contact with the zero-valent iron media in a range of between about 5 mg/L and about 50 mg/L.

32 . The method of claim 30 , wherein the source of Fe 2+ ions is added to the fluidized bed reactor at a flow rate that maintains the concentration of Fe 2+ ions in the wastewater coming into contact with the zero-valent iron media in a range of between about 0 mg/L and about 5 mg/L.

33 . The method of claim 23 , wherein a pH adjustment agent is added to the fluidized bed reactor at a flow rate that maintains a pH of wastewater in the fluidized bed reactor between about 6.0 and about 8.0.

34 . The method of claim 23 , further comprising contacting the wastewater with an oxidizer prior to introducing the wastewater into the fluidized bed reactor.

35 . A method of increasing the selenium removal efficiency of a fluidized bed reactor including a zero valent iron media, the method comprising relocating a site of injection of an oxygen containing gas from a location proximate a top of the fluidized bed reactor to a location in a reaction zone defined about a mixer in a lower portion of the fluidized bed reactor.

Assignments (4)
RELEASE OF SECURITY INTEREST Recorded May 26, 2023
From: JPMORGAN CHASE BANK N.A., AS COLLATERAL AGENT
To: EVOQUA WATER TECHNOLOGIES LLC; NEPTUNE BENSON, INC.
Reel/Frame 063787/0943 →
SECURITY INTEREST Recorded Apr 7, 2021
From: EVOQUA WATER TECHNOLOGIES LLC; NEPTUNE BENSON, INC.
To: JPMORGAN CHASE BANK, N.A., AS COLLATERAL AGENT
Reel/Frame 055848/0689 →
ASSIGNMENT OF ASSIGNOR'S INTEREST Recorded Sep 26, 2017
From: HUANG, YONGHENG
To: THE TEXAS A&M UNIVERSITY SYSTEM
Reel/Frame 043688/0466 →
ASSIGNMENT OF ASSIGNOR'S INTEREST Recorded Sep 26, 2017
From: WISMER, MICHAEL W.; MASON, SAMUEL A.
To: EVOQUA WATER TECHNOLOGIES LLC
Reel/Frame 043688/0640 →