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Biotrickling fjltration as sustainable technology for biogas - - PowerPoint PPT Presentation

Biotrickling fjltration as sustainable technology for biogas upgrading to renewable fuel Eric Santos-Clotas* , Alba Cabrera-Codony, Ellana Boada, Frederic Gich, Maria J. Martin *eric.santos@udg.edu 28 th June, 2019 7 th International


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SLIDE 1

Biotrickling fjltration as sustainable technology for biogas upgrading to renewable fuel

7th International Conference on Sustainable Solid Waste Management

Eric Santos-Clotas*, Alba Cabrera-Codony, Ellana Boada, Frederic Gich, Maria J. Martin

*eric.santos@udg.edu

28th June, 2019

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SLIDE 2

CONTENTS

Introduction Objectives Materials and Methods Results Conclusions

1

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SLIDE 3

Objectives

Materials & Methods

Results

Conclusions

Introductio n

2

Wastewater treatment plant Landfjlls

Anaerobic digestion

CH4 CO2 Renewable energies

Hydrogen sulphide

Volatile organic compounds

BIOGAS

SILOXANES

[10 - 100 mg m-3] Energetic valorisation of biogas Heat and electricity Gas grid injection Car fuel Combustion reactions: Siloxanes  SiO2 Build-up of silica layers Abrasion of engine parts Inhibits conduction/lubrication

DSi

VOLATILE METHYL SILOXANES

LSi

[1,000 – 20,000 ppmv]

  • Chemical stability
  • Hydrophobicity
  • Low surface tension
  • Aroma free
  • Exempts from VOC

regulations

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SLIDE 4

Objectives

Materials & Methods

Results

Conclusions

Introductio n

3

BIOGAS

H2S H2O Siloxan es

Adsorption [Steam- AC]

Energy recovery system

Frequent replacement

  • f exhausted material

Disposal of spend carbon as hazardous waste High removal effjciency Mature technology

OPERATING COSTS Alternative technologies

Reduce investment and operation costs Increment treatment capacities Low energy and chemicals demand Scarce reports at LABSCALE 40% D4 removal at EBRT 20 min (Popat & Deshusses

2008)

Low mass transfer due to low water solubility EBRT s that high would not be viable at industrial scale

Biotrickling fjlter

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SLIDE 5

Materials & Methods

Results

Conclusions Introduction Objectives

4

Anoxic biodegradation of siloxane D4 in a lab-scale biotrickling fjlter. Co-treatment of siloxanes and other biogas impurities in the BTF Infmuence of the EBRT upon the compounds removal in

  • rder to optimize the performance of the system.

Role of an activated carbon layer  enhancing the mass transfer of water insoluble compounds

I II III IV

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SLIDE 6

Materials & Methods

Results

Conclusions Introduction

Objectives

Stage Period [days] C- Source EBRT [min] Packing media I 0-42 D4 14.5 Lava rock II

  • 1

43-85 Multi 14.5 Lava rock

  • 2

86-107 Multi 10.1 Lava rock

  • 3

108- 128 Multi 7.3 Lava rock

  • 4

129- 152 Multi 4 Lava rock III 153- 186 Multi 12 Lava rock+AC IV 187- 207 Multi 2 AC

Biotrickling fjlter

Operating conditions Experiment al set up Compoun d Formula MW

[g mol-

1]

Solubilit y

[mg L-1]

Inlet conc.

[mg m-3]

Hexane

86 9.5 375 ± 18

T

  • luene

92 526 24 ± 2

Limonene

136 13.8 220 ± 11

D4

297 0.056 54 ± 3

D5

371 0.017 102 ± 4 5 Supplementation of the packing bed with 20% of a Wood-based H3PO4-ACTIVATED CARBON

Anoxic conditions NO3

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SLIDE 7

Materials & Methods

Results

Conclusions Introduction

Objectives

Stage Period [days] C- Source EBRT [min] Packing media I 0-42 D4 14.5 Lava rock II

  • 1

43-85 Multi 14.5 Lava rock

  • 2

86-107 Multi 10.1 Lava rock

  • 3

108- 128 Multi 7.3 Lava rock

  • 4

129- 152 Multi 4 Lava rock III 153- 186 Multi 12 Lava rock+AC IV 187- 207 Multi 2 AC

Biotrickling fjlter

Operating conditions Experiment al set up Compoun d Formula MW

[g mol-

1]

Solubilit y

[mg L-1]

Inlet conc.

[mg m-3]

Hexane

86 9.5 375 ± 18

T

  • luene

92 526 24 ± 2

Limonene

136 13.8 220 ± 11

D4

297 0.056 54 ± 3

D5

371 0.017 102 ± 4 6 Analytical procedures Gas streams – Gas chromatography

  • Flame Ionization detector

(FID)

  • Mass spectrometry (MS)

Silicon compounds

  • T
  • tal Silica: Inductively coupled

plasma-optical emission spectroscopy (ICP-OES)

  • Silicic acid: colorimetric test

NO3

  • , NO2
  • : Ion chromatography with conductivity

detector Biomass: Scanning electron microscopy (SEM)

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SLIDE 8

Materials & Methods

Results

Conclusions Introduction

Objectives

BTF operation – stage I: D4 only

Average 14% removal effjciency SEM analysis of the lava rock

BTF

  • peration

– stage II: multicompound

A Hexane T
  • luene
D4 Limonene EBRT [min] Rem oval effj c ie n c y [%]

7

Limonene and toluene 100% RE at all EBRT s

  • Max. 16% RE of hexane at longest

EBRT D5 RE from 15 to 37% at EBRT 4 to 14.5 min D4 removal ranged 8-14%

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SLIDE 9

Materials & Methods

Results

Conclusions Introduction

Objectives

50 100 150 200 250 300 350 400 450 500 100 200 300 400 Hexane

Time [min] Concentration [mg m-3]

Activated carbon SEM images BEFORE AFTER 30 days BTF packing bed supplemented with activated carbon 8

BTF operation – role of the AC

After 20 days:

  • D5

and hexane REs increased up to 45 and 44%, respectively

  • Higher

presence

  • f

silanediols, catalytic AC

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SLIDE 10

Materials & Methods

Results

Conclusions Introduction

Objectives

Metabolite Formula MW

[g mol-1]

Analytical ions m/z [abundance ] Dimethylsilan ediol [DMSD] 92

77 [99.9] 45 [14.6] 78 [6.6]

T etramethyl- 1,3- disiloxanediol 166

133 [99.9] 151 [71.2] 135 [22.6]

Hexamethyl- 1,5- trisiloxanediol 240

207 [99.9] 208 [21.1] 209 [17.0]

2-careen 136

93 [99.9] 121 [96.8] 136 [66.9]

α-terpinene 136

121 [99.9] 93 [84.7] 136 [42.6]

P-cymene 134

119 [99.9] 91 [34.7] 134 [23.8]

0,0 0,2 0,4 0,6 0,8 1,0 30 60 90 120 150

A

T

  • luene

C/C0 Metabolite GC area [µV·min]

1 2 3 4 5 6 7 8 9 10 0,0 0,2 0,4 0,6 0,8 30 60 90 120

B

Time [hours] C/C0 Metabolite GC area [µV·min]

TRICKLING RECIRCULATION ON OFF ON METABOLITES IDENTIFICATION 9 BTF operation with lava rock at EBRT 10 min BTF operation with AC at EBRT 2 min 5 h

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SLIDE 11

Materials & Methods

Results

Conclusion s

Introduction

Objectives

  • A complete removal of toluene and limonene was accomplished by an anoxic lab-scale

BTF inoculated with Pseudomonas sp. even at short EBRTs.

  • The removal of hexane, D4 and D5 was correlated to their Henry’s law coeffjcients,

which indicated that mass transfer limitations challenged their abatement in the BTF .

  • The supplementation of the BTF packing bed with Activated Carbon enhanced

the transference of hexane and D5 to the microbial community.

  • AC supplementation enabled BTF operation at reduced EBRTs while displaying a high

robustness towards interruptions in the trickling irrigation.

10

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SLIDE 12

Biotrickling fjltration as sustainable technology for biogas upgrading to renewable fuel

7th International Conference on Sustainable Solid Waste Management

28th June, 2019 Thank you for your attention!