Response of a multi species linuron degrading bacterial biofilm to - - PDF document

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Response of a multi species linuron degrading bacterial biofilm to - - PDF document

Response of a multi species linuron degrading bacterial biofilm to different nutrient conditions and dissolved organic matter Benjamin Horemans, Dr. Philip Breugelmans and Prof. Dirk Springael Introduction Pesticides are essential for


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Response of a multi‐species linuron‐degrading bacterial biofilm to different nutrient conditions and dissolved organic matter

Benjamin Horemans, Dr. Philip Breugelmans and Prof. Dirk Springael

Introduction Pesticides are essential for agricultural practices but leads to contamination of groundwater and surface water Threath to drinkwater production and ecosystems Biodegradation plays important role in natural attenuation

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Model pesticide

  • Linuron = systemic herbicide
  • Toxic for aquatic organisms

Model consortium:

  • Isolated from soil
  • Synergistic degradation of linuron

by three‐species consortium under planktonic conditions

(Dejonghe et al., 2003)

Variovorax sp. WDL1

  • C. testosteroni WDL7

Variovorax

  • sp. WDL1
  • H. sulfonivorans WDL6

Synergistic interaction Linuron‐degrading consortium Labscale simulation growing communities as a biofilm in flow cells Acquisition of 3D‐images with CLSM and study of architecture and composition of biofilms Under natural conditions microbial communities grow predominantly as biofilms Synergistic interaction Linuron‐degrading consortium

  • P. Dirckx (CBE)
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Variovorax sp. WDL1

  • H. sulfonivorans WDL6‐Yfp
  • C. testosteroni WDL7‐Rfp

+ +

Confocal Laser Scanning Microscopy (CLSM) High‐Performance Liquid Chromatography (HPLC) Labscale biofilm system Linuron‐degrading consortium

0,00 0,02 0,04 0,06 0,08 0,10 0,12 5 10 15 20 25 30 35 40

Day 0 Day 5 Day 31 Day 13 Day 24

0,00 0,02 0,04 0,06 0,08 0,10 0,12 5 10 15 20 25 30 35 40 Time (days) Linuron or 3,4‐DCA concentration (mmol L‐1)

  • Synergism under sessile

conditions

  • Required for complete

linuron degradation

WDL1 only Consortium

Consortium biofilm development Linuron‐degrading consortium

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Linuron (0.1 mM) Citrate (0.1 mM)

6,8 17,3 75,9

46,3 10,0 43,7

Spatial organization under linuron‐fed conditions reflects metabolic interactions

Structure‐function relationship Linuron‐degrading consortium

MM + Linuron + alternative C and/or N source HPLC

Linuron degradation Activity Effect of Additional C and/or N sources

Linuron or 3,4‐DCA degradation (%) ‐N +N +N ‐N +N ‐N 0.1 mM linuron 0.1 mM linuron + 0.1 mM citrate 0.1 mM linuron + 5 mM citrate

3,4‐DCA Linuron

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Linuron Linuron + N Linuron + 0.1 mM citrate Linuron + N + 0.1 mM citrate Linuron + 5 mM citrate Linuron + N + 5 mM citrate

Biofilm Characteristics Effect of Additional C and/or N sources

Linuron medium Alternative media (no linuron) HPLC ~30 days 6 days

Initial irrigation medium Intermediate irrigation medium Final irrigation medium Operation time (days) Linuron degradation (%) 3,4‐DCA degradation (%) 1 0.1 mM linuron C‐ and N‐starved medium 0.1 mM linuron 11 66 (± 3) 84 (± 3) 2 0.1 mM linuron C‐starved medium 0.1 mM linuron 11 70 (± 4) 84 (± 2) 3 0.1 mM linuron N‐starved medium 0.1 mM linuron 14 72 (± 2) 85 (± 2) 4 0.1 mM linuron Alternative C and N source (0.1 mM citrate + N) 0.1 mM linuron 11 86 (± 2) 90 (± 3)

Linurondegradation Activity

Effect of Temporal Exposure to starvation or alternative C and N source

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Linuron C and N starvation C starvation N starvation N + 0.1 mM citrate Linuron

Biofilm Characteristics

Effect of Temporal Exposure to starvation or alternative C and N source

Source of carbon, energy and nutrients (N, P) for heterotrophic microbial communities Quantity = concentration Quality = biodegradability community composition and abundance enzymatic activity adaptation

? Pesticide degradation

Carbon and Energy Source Dissolved Organic Matter (DOM) DOM

  • Citric acid
  • Leachate of maize leaves
  • Extract of soil‐incubated maize leaves

Increasing recalcitrance

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Planktonic conditions Effect of DOM Quality and Quantity Citric acid Leachate Incubated

Linuron degradation 3,4‐DCA accumulation

Linuron 3,4‐DCA No TOC 0.4 mM DOC 1.6 mM DOC

Effect of DOM on linuron degradation in MM + 0.08 mM linuron by strain Variovorax sp. WDL1 under planktonic conditions Presence of easily‐degrabable carbon sources, besides linuron, negatively affects linuron‐degrading activity of consortium biofilms (concentration dependent) No full recovery of linuron‐degrading activity of consortium biofilms after intermittent exposure to nutrient‐starved or nutrient‐rich media changes in biofilm biomass, organization and composition particular biofilm characteristics for each condition DOM of natural origin enhances linuron‐degrading activity of Variovorax sp. WDL1 under planktonic conditions Conclusions

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Thank you for your attention