1
Bacteria Encapsulation for Wastewater Treatment Alexandra Applegate 1 , Jacqueline Hohenstein 1 , Alik McCoy 1 , Cherish Vance 2 Advisor: Dr. Kung-Hui Chu 1 Graduate Assistants: Kun-Ching Cho 1 1 Zachry Department of Civil Engineering, 2 Biological and Agricultural Engineering, Texas A&M University, College Station, TX. Discuss Results Problems Faced Future Applications Human activities related to nitrogen have caused an overarching problem - an imbalance in the global nitrogen cycle. Through conventional wastewater treatment processes, mainly a combination of aerobic nitrification and anoxic denitrification processes, ammonia and other forms of nitrogen can be converted into nitrogen gas and return back to the nitrogen cycle. However, this approach not only requires significant input of energy and oxygen but also produces greenhouse gas like nitrous oxides during denitrification. A novel way to reduce energy and oxygen inputs while minimizing greenhouse production for nitrogen removal is necessary. Originally our research wanted to encapsulate ANaerobic AMMonium- OXidizing bacteria (anammox) and ammonia-oxidizing bacteria – AOB with PEG into a single reactor. The challenge of such an approach is that these bacteria grow extremely slow and require a much longer residence time than a traditional treatment process permits. To accelerate the research Nitrite- oxidizing bacteria -NOB was used to test the effectiveness of the encapsulation process. The specific objectives of this study are to 1) enrich AOB and NOB, 2)Keep AOB and NOB alive after they have been encapsulated with PEG, and 3) incorporate a novel reactor that will deplete ammonia efficiently and compare qualitatively to the suspended growth process commonly performed in wastewater treatment processes. This phase of the project has been extensive, yet the results are promising. We have enriched AOB and NOB effectively (Fig 1). To provide a long solid retention time for the AOB and NOB, we have also successfully encapsulated them in polyethylene glycol (PEG) gel carriers. This phase has proven that after encapsulation cells are alive. Using an ammonia probe, nitrite reagents and optical density calculation test provided reason to conclude that encapsulation does not exterminate AOB and NOB. Eventually when the process of enriching anammox had been mastered, this study aims to develop Single-reactor Nitrification and Ammonia Removal using Encapsulated ANAMMOX, or SNARE ANAMMOX, completing the nitrogen cycle. The expected results for the next phase include the providing a quantitative value for cell growth using PCR analysis, understanding how to enrich ammonium-oxidizing bacteria, and the efficient removal of nitrogen from synthetic wastewater using the proposed SNARE-ANAMMOX process. The anticipated benefits of this approach are lower energy input, less oxygen demand, reduced creation of sludge, reduced production of greenhouse gas, and high removal rate of nitrogen. ABSTRACT RESULTS Discussion and Conclusion PROPOSED APPROACH Enrich ammonia-oxidizing bacteria (AOB) and nitrite- oxidizing bacteria (NOB) separately in a sequential batch reactors Double encapsulate the AOB and NOB in gel carriers that will… The bacteria in the gel carriers were placed in a reactor with AOB growth medium and monitored Simultaneously, bacteria that were not encapsulated were placed in a suspended growth reactor for comparison Measurement of ammonia levels in the reactors using an ammonia probe. BACKGROUND To enrich and encapsulate AOB and NOB To incorporate the encapsulated cells into a reactor To compare the this reactor to a suspended growth reactor OBJECTIVES ACKNOWLEDGEMENTS The team thank Lazar Kish and Dr. Jun Kameoka for their assistance in the encapsulation of the AOB and NOB. Conventional wastewater treatment processes rely on aerobic nitrification and anaerobic denitrification to remove nitrogen in wastewater. Photo of Encapsulated AOB and NOB Nitrosomonas: an ammonia- oxidizing bacterium NH 4 + + 1.5 O 2 NO 2 - + 2H + +H 2 O e- donor: NH 4 + e- acceptor: O 2 C-source: HCO 3 - Nitrification is a two-step process NH 4 + + 1.5 O 2 NO 2 - + 2H + +H 2 O (by Ammonia-oxidizing bacteria (AOB) NO 2 - + 0.5 O 2 NO 3 - (by Nitrite-oxidizing bacteria (NOB)) Aerobic/ Nitrification Anoxic Denitrification Influent Effluent Sludge Return activated sludge NH 4 + NO 2 - NO 3 - N 2 O 2 O 2 NO N 2 O Denitrification Nitrification Nitrification and Denitrification: How do they work? Challenges High energy and O 2 input. Production of greenhouse gas (N 2 O) Denitrification: NO 3 - + Organics N 2 Our Solution: Improve the Efficiency of Wastewater Treatment Processes with Encapsulated Bacteria Possible Benefits of using Encapsulated Bacteria? Longer Retention time Ammonia Measurement What do we mean by Encapsulation? Within each gel carrier, the NOB are encapsulated in a smaller carrier, surrounded by AOB and then both bacteria are encapsulated in a larger carrier Enriching AOB and NOB

Bacteria Encapsulation for Wastewater Treatment · Bacteria Encapsulation for Wastewater Treatment Alexandra Applegate1, Jacqueline Hohenstein1, Alik McCoy1, Cherish Vance2 Advisor:

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Page 1: Bacteria Encapsulation for Wastewater Treatment · Bacteria Encapsulation for Wastewater Treatment Alexandra Applegate1, Jacqueline Hohenstein1, Alik McCoy1, Cherish Vance2 Advisor:

Bacteria Encapsulation for Wastewater Treatment Alexandra Applegate1, Jacqueline Hohenstein1, Alik McCoy1, Cherish Vance2

Advisor: Dr. Kung-Hui Chu1 Graduate Assistants: Kun-Ching Cho1 1Zachry Department of Civil Engineering, 2Biological and Agricultural Engineering, Texas A&M University, College Station, TX.

Discuss Results Problems Faced Future Applications

Human activities related to nitrogen have caused an overarching problem - an imbalance in the global nitrogen cycle. Through conventional wastewater treatment processes, mainly a combination of aerobic nitrification and anoxic denitrification processes, ammonia and other forms of nitrogen can be converted into nitrogen gas and return back to the nitrogen cycle. However, this approach not only requires significant input of energy and oxygen but also produces greenhouse gas like nitrous oxides during denitrification. A novel way to reduce energy and oxygen inputs while minimizing greenhouse production for nitrogen removal is necessary. Originally our research wanted to encapsulate ANaerobic AMMonium-OXidizing bacteria (anammox) and ammonia-oxidizing bacteria – AOB with PEG into a single reactor. The challenge of such an approach is that these bacteria grow extremely slow and require a much longer residence time than a traditional treatment process permits. To accelerate the research Nitrite-oxidizing bacteria -NOB was used to test the effectiveness of the encapsulation process. The specific objectives of this study are to 1) enrich AOB and NOB, 2)Keep AOB and NOB alive after they have been encapsulated with PEG, and 3) incorporate a novel reactor that will deplete ammonia efficiently and compare qualitatively to the suspended growth process commonly performed in wastewater treatment processes. This phase of the project has been extensive, yet the results are promising. We have enriched AOB and NOB effectively (Fig 1). To provide a long solid retention time for the AOB and NOB, we have also successfully encapsulated them in polyethylene glycol (PEG) gel carriers. This phase has proven that after encapsulation cells are alive. Using an ammonia probe, nitrite reagents and optical density calculation test provided reason to conclude that encapsulation does not exterminate AOB and NOB. Eventually when the process of enriching anammox had been mastered, this study aims to develop Single-reactor Nitrification and Ammonia Removal using Encapsulated ANAMMOX, or SNARE ANAMMOX, completing the nitrogen cycle. The expected results for the next phase include the providing a quantitative value for cell growth using PCR analysis, understanding how to enrich ammonium-oxidizing bacteria, and the efficient removal of nitrogen from synthetic wastewater using the proposed SNARE-ANAMMOX process. The anticipated benefits of this approach are lower energy input, less oxygen demand, reduced creation of sludge, reduced production of greenhouse gas, and high removal rate of nitrogen.

ABSTRACT

RESULTS

Discussion and Conclusion

PROPOSED APPROACH Enrich ammonia-oxidizing bacteria (AOB) and

nitrite- oxidizing bacteria (NOB) separately in a sequential batch reactors

Double encapsulate the AOB and NOB in gel carriers that will…

The bacteria in the gel carriers were placed in a reactor with AOB growth medium and monitored

Simultaneously, bacteria that were not encapsulated were placed in a suspended growth reactor for comparison

Measurement of ammonia levels in the reactors using an ammonia probe.

BACKGROUND

• To enrich and encapsulate AOB and NOB • To incorporate the encapsulated cells into a reactor • To compare the this reactor to a suspended growth reactor

OBJECTIVES ACKNOWLEDGEMENTS

• The team thank Lazar Kish and Dr. Jun Kameoka for their assistance in the encapsulation of the AOB and NOB.

• Conventional wastewater treatment processes rely on aerobic nitrification and anaerobic denitrification to remove nitrogen in wastewater.

Photo of Encapsulated AOB and NOB

Nitrosomonas: an ammonia- oxidizing bacterium NH4

+ + 1.5 O2 NO2- + 2H+

+H2O

e- donor: NH4+

e- acceptor: O2 C-source: HCO3

-

Nitrification is a two-step process • NH4

+ + 1.5 O2 NO2- + 2H+ +H2O

(by Ammonia-oxidizing bacteria (AOB) • NO2

- + 0.5 O2 NO3-

(by Nitrite-oxidizing bacteria (NOB))

Aerobic/Nitrification

AnoxicDenitrification

Influent Effluent

Sludge

Return activated sludge

NH4+ NO2

- NO3-

N2

O2 O2

NO N2O

Denitrification

Nitrification

• Nitrification and Denitrification: How do they work?

• Challenges High energy and O2 input. Production of greenhouse gas (N2O)

Denitrification: • NO3

- + Organics N2

Our Solution: Improve the Efficiency of Wastewater Treatment Processes with Encapsulated Bacteria

Possible Benefits of using Encapsulated Bacteria?

Longer Retention time

Ammonia Measurement

What do we mean by Encapsulation?

Within each gel carrier, the NOB are

encapsulated in a smaller carrier, surrounded by AOB and then both

bacteria are encapsulated in a larger carrier

Enriching AOB and NOB