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Understanding the role of Tetrasphaera in enhanced biological phosphorus removal N. Rey, M. Badia, A. Guisasola, J. A. Baeza Departament dEnginyeria Qumica Biolgica i Ambiental, Escola dEnginyeria, Universitat Autnoma de Barcelona,


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Understanding the role of Tetrasphaera in enhanced biological phosphorus removal

  • N. Rey, M. Badia, A. Guisasola, J. A. Baeza

Departament d’Enginyeria Química Biològica i Ambiental, Escola d’Enginyeria, Universitat Autònoma de Barcelona, 08193, Bellaterra, Barcelona 13th IWA Specialized Conference on Small Water and Wastewater Systems 14-16 September, 2016 ATHENS, GREECE

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Introduction

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Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

Candidatus Accumulibacter phosphatis Most well-known and studied PAO Full-scale EBPR plants Other putative PAOs Genus Tetrasphaera EBPR is an economical, efficient and sustainable way to remove phosphorus from the wastewater

EBPR

Alternating anaerobic and aerobic conditions

PAOs

Uptake and storage of poly-phosphate

PHA

Take up simple carbon sources

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Introduction

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Amino acids Low concentrations of volatile fatty acids Lab-scale Volatile fatty acids COD consumed in the anaerobic reactor/phase Microbiological techniques

Enrichment of Accumulibacter (PAOs)

Full-scale

Tetrasphaera proliferation

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

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Objective

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  • To gain knowledge on the new PAO genus Tetrasphaera by obtaining

an enriched culture at lab-scale

  • Two reactor configurations:
  • Sequencing batch reactor
  • Continuous pilot plant system with A2/O configuration

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

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Time (days)

20 40 60 80 100

Phosphate concentration (mg P·L-1)

10 20 30 40

N2 increase G+A G+A G G+A 44 mg O2/L 71 mg O2/L 113 mg O2/L 71 mg O2/L

Results: SBR operation

3

V = 10L Synthetic influent: 10 mg P-PO4

  • 3/L, 44-113 mg COD/L

Aspartate + Glutamate

Initial time End of anaerobic phase End of aerobic phase

Single batch experiments Glutamate Aspartate

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

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Results: SBR operation

3

V = 10L Synthetic influent: 10 mg P-PO4

  • 3/L, 44-113 mg COD/L

Aspartate + Glutamate

Initial time End of anaerobic phase End of aerobic phase

Excess of carbon source Glutamate leakage to the aerobic phase System failure

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

Time (days)

20 40 60 80 100

Phosphate concentration (mg P·L-1)

10 20 30 40

N2 increase G+A G+A G G+A 44 mg O2/L 71 mg O2/L 113 mg O2/L 71 mg O2/L

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Results: A2/O operation

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V = 146L Synthetic influent: 10 mg P-PO4

  • 3/L, 50 mg N-NH4

+/L and

400 mg COD/L Glutamate

Time (days)

100 200 300 400

Phosphate concentration (mg·L

  • 1

)

20 40 60 80 100

P-removal efficiency (%)

20 40 60 80 100

P-removal efficiency>95% Batch deteriorated glutamate Excesive NO3

  • input

in the anaerobic reactor

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016 P-PO4-3 Anaerobic (mg/L) P-PO4-3 Effluent (mg/L) P-removal efficiency (%)

Glutamate as carbon and nitrogen source

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Results: Batch experiments with the SBR sludge

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PHA & Glycogen quantification

PHA: 0.69 mmol C/gVSS Glycogen: 0.47 mmol C/gVSS PAO-enriched cultures: PHA production: 2.67 mmol C/gVSS Glycogen consumption: 1.30 mmol C/gVSS

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

Time (min)

50 100 150 200 250 300 350

TOC (mg C/L) Phosphate (mg P/L)

10 20 30 40

PHA and glycogen (mmol C/g VSS)

1 2 3 4 5

Anaerobic Aerobic P (mg/L) TOC (mg/L) Glycogen (mmol C/g VSS) PHA (mmol C/g VSS)

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Results: Batch experiment with the A2/O sludge

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PHA & Glycogen quantification

PHA: 0.62 mmol C/gVSS Glycogen: 0.06 mmol C/gVSS

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

PAO-enriched cultures: PHA production: 2.67 mmol C/gVSS Glycogen consumption: 1.30 mmol C/gVSS

Time (min)

50 100 150 200 250 300 350

Phosphate (mg P/L) and COD (mg/L)

20 40 60 80 100

PHA and glycogen (mmol C/mg VSS)

0.0 0.5 1.0 1.5 2.0 2.5

Anaerobic Aerobic P (mg/L) COD (mg/L) Glycogen (mmol C/g SSV) PHA (mmol C/g SSV)

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Results: Comparison between configurations

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mmol C/g VSS SBR A2/O COD consumed 3.436 8.87 PHA 0.692 0.621 Glycogen 0.476 0.066 Total=PHA + Glycogen 1.168 0.687 Carbon recovery ratio 0.34 0.08

Other storage routes should be studied

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

Anaerobic PHA and glycogen production

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Results: Literature comparison

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Study Prel/Cupt (mol P/mol C) PHAprod/Cupt (mol C/mol C) Glycprod/Cupt (mol C/mol C) Enriched PAO Kapagiannidis et al. (2013) 0.64 1.10 Consumption (-0.41) Tayà et al. (2013) 0.34 1.47 Consumption (-0.49) This study SBR 0.27 0.20 0.14 A2/O 0.21 0.07 0.01

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

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Results: Bacterial community assessment

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Tetrasphaera Clone ASM31 Uncultured Tetraspahera SBR PAO GAO

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Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

31% 21% 30% 13% All bacteria Specific bacteria Tetrasphaera Clade II Tetrasphaera Clone ASM47

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Results: Bacterial community assessment

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A2/O pilot plant PAO GAO

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

26% 1% 39% 27% All bacteria Specific bacteria Tetrasphaera Clone ASM31 Uncultured Tetraspahera Tetrasphaera Clade II Tetrasphaera Clone ASM47

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Results: Bacterial community assessment

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PAOMix GAOMix Tetrasphaera SBR 36 ± 1% 21 ± 1% 43 ± 9% A2/O plant 26 ± 4% 1 ± 1% 66 ± 5%

Why do we detect the presence of PAO and GAO if we fed the reactor with glutamate for more than 400 days?

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

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Results: Bacterial community assessment

3

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

Anaerobic fermentation routes for glutamate

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Further work

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We are still operating the A2/O pilot plant with glutamate We are working with this enriched-tetrasphaera culture in

  • rder to better understanding this new PAO genus

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

We will perform batch assays with different carbon sources and different electron acceptors We are waiting for the pyrosequencing results

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Conclusions

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  • Successful enrichment of sludge in Tetrasphaera using glutamate as

sole carbon source was obtained for the first time.

  • Better results and more stability was achieved with continuous pilot

plant with respect to SBR.

  • Fermentation products of glutamate did not allow to obtain a highly

Tetrasphaera-enriched culture.

  • The increase of PHA and glycogen during the anaerobic phase only

accounted a small percentage of the carbon source consumed.

  • Other storage routes should be studied to identify the fate of the

carbon source stored under anaerobic conditions.

Understanding the role of Tetrasphaera in EBPR – N. Rey et al. SWWS 2016

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Ackno knowledgments ledgments

CTQ2014-60495-R with funds from the Fondo Europeo de Desarrollo Regional (FEDER)

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Thank you for your attention!

talia Rey talia Rey Marina Badia Marina Badia Albert Guisasola Albert Guisasola Juan Antonio Baeza uan Antonio Baeza

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Understanding the role of Tetrasphaera in enhanced biological phosphorus removal

  • N. Rey, M. Badia, A. Guisasola, J. A. Baeza

Departament d’Enginyeria Química Biològica i Ambiental, Escola d’Enginyeria, Universitat Autònoma de Barcelona, 08193, Bellaterra, Barcelona