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Alginate Encapsulated Nanoparticle-Microorganism System for Trichloroethylene Remediation
Outline ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Introduction
Global Nano Market US$ in Billion (2015) Source: NSF
Nanoparticles (NPs) ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],ASTM International, 2006;  Liu et al., 2006
Applications of Nanoparticles ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
NPs for Environmental Remediation  ,[object Object],[object Object],[object Object],[object Object],[object Object]
NPs for Water Remediation Nanoparticles Contaminant Reference Nano Zeolites Toluene, nitrogen dioxide Song et al. (2004) Carbon nanotubes (CNTs) p-nitrophenol, benzene, toluene, heavy metal ions,dimethylbenzene Jin et al. (2007) Bimetallic nanoparticles (Pd/Fe) PCBs, chlorinated methane, ethene, Trichloroethylene (TCE) Xu and Bhattacharyya (2005) Xu and Zhao (2007) Wang and Zhang (1997) Kim et al. (2010) Ni/Fe and Pd/Au nanoparticles TCE and PCBs He and Zhao (2005) TiO 2  photocatalyst Heavy metal ions Pentachlorophenol (PCP) Pena et al. (2005) Quan et al. (2005) NZVI Herbicides (Alachlor) Thompson et al. (2010) NZVI Nitrate Bezbaruah et al. (2009) NZVI TCE Bezbaruah et al. (2011)
Why NZVI? ,[object Object],[object Object],[object Object],[object Object],[object Object],Image Credit :  Matheson, and Tratnyek, 1994  Fe 0     Fe  2+  + 2e -   R-X + 2e -   + H +     R-H + X -   Bezbaruah et al. 2009; Thompson 2010; Zhang 2003
Contaminant ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],U.S. EPA, 2011
TCE Contaminated Sites ,[object Object],[object Object],[object Object],[object Object],USEPA 2007
In-situ Injection Injection Well Groundwater Flow TCE Contaminated plume NZVI Aquifer
Present Study
Challenges ,[object Object],[object Object]
More on TCE Remediation Methods ,[object Object],[object Object],[object Object],[object Object]
Objectives ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Hypotheses ,[object Object],[object Object]
TCE Degradation Mechanism - NZVI C=C  Cl Cl H Cl Fe 0 Cl - e - C=C  H Cl H Cl Fe 0 Cl - e - C=C  H Cl H H Fe 0 Cl - e - C=C  H H H H TCE DCE VC Ethene
Model Microorganisms ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],www.miller-mccune.com http://gtresearchnews.gatech.edu/
Prior Work
P. putida  F1 Interactions with NZVI Shabnam, 2011
E. coli  8739 interactions with NZVI
Experimental Design
Experimental Design Microorganisms Pp  F1 D.  BAV1 Encapsulated Microorganisms Combined NZVI-Microorganism System TCE Degradation NZVI Bare Encapsulated Encapsulated NZVI Research Phase I
Research Phase I Encapsulated NZVI System
Research Phase I ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Synthesis of NZVI ,[object Object],[object Object],TEM image of clustered nanoparticles Krajangpan et al. 2009; Bezbaruah et al. 2009; Bezbaruah et al. 2011 a b a  and  b : Dried NZVI XRD spectrum of NZVI
Encapsulation ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Why alginate? ,[object Object],[object Object],[object Object],[object Object],[object Object],Hill and Khan, 2008
Preparation of Capsules a : Capsules  30 mg NZVI 1.33% Iron loss Bezbaruah et al., 2011 b b : Encapsulated NZVI  4 g Maltodextrin 6 mL DI water 0.25 g CaCl 2 50 mL alginate Peristaltic pump Stirrer 6 cm b a
Batch Experiments ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],Capsules TCE Solution  40 mL Vial
Diffusion Study Results ,[object Object],[object Object]
TCE Degradation Batch Studies Encapsulated NZVI ,[object Object],[object Object],Blank Control Analysis Capsules TCE Solution  TCE Solution TCE Solution + Bare NZVI
TCE Degradation Batch Study  ,[object Object],[object Object],[object Object]
TCE Degradation Kinetics TCE degradation followed  First Order Kinetics  for both bare and encapsulated NZVI No significant difference   Bare and Encapsulated NZVI (95% CI, Two Way ANOVA ) Bezbaruah et al., 2011 Batch Initial TCE concentration mg L -1 Reaction rate constant R 2 k  obs 10 -2  min -1 k sa 10 -3  L m -2  min -1 Bare NZVI 1 2.92 1.6 0.9689 10 2.35 1.3 0.9801 30 1.53 0.8 0.9897 40 2.24 1.2 0.9868 Encapsulated NZVI 1 3.23 1.7 0.9832 10 2.45 1.3 0.9491 30 1.92 1.0 0.9921 40 2.21 1.2 0.9425
Encapsulated NZVI: pH Observations ,[object Object],[object Object],[object Object]
Shelf-life Study ,[object Object],[object Object]
Research Phase I-Summary ,[object Object],[object Object],[object Object],[object Object]
Work Remaining Microorganisms Pp F1 D.  BAV1 Encapsulated Microorganisms Combined NZVI-Microorganism system TCE Degradation NZVI Bare Encapsulated Encapsulated NZVI
Experimental Design Microorganisms Pp F1 D.  BAV1 Encapsulated Microorganisms Combined NZVI-Microorganism system TCE Degradation NZVI Bare Encapsulated Encapsulated NZVI Research Phase II
Combined NZVI-Microorganism System
TCE Degrading Bacteria Microorganism Method of Removal End Product Reference Pseudomonas putida  F1 Direct Oxidation Co-metabolism ETH (Sun and Wood 1996); (Kim et al. 2010b); (Radway et al. 1998) Clostridium bifermentans  DPH-120 Co-metabolism c-DCE (Chang et al. 2000) Dehalospirillum multivorans Direct Oxidation c-DCE (Neuman et al.1994) Dehalococcoides ethenogenes  195 Reductive  dechlorination ETH (Maymo-Gatell et al. 1999), (Fennell et al. 2001) Dehalococcoides  BAV1 Reductive dechlorination ETH (Krajmalnik-Brown et al. 2004; Maymo-Gatell et al. 1999),(He et al. 2003) Dehalococcoides  VS Reductive dechlorination ETH (Cupples et al. 2003) Dehalococcoides  FL2 Reductive dechlorination ETH (El Fantroussi  et al. 1998)
Model Microorganisms ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],www.miller-mccune.com http://gtresearchnews.gatech.edu/
Research Phase II Combined NZVI- Pp  F1 System
Research Phase II ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Pseudomonas putida  F1 strain ,[object Object],[object Object],www.miller-mccune.com
Growth Curve-  Pseudomonas putida  F1 P. putida  incubated at 30 o C in TSB media and shaken for  24 h 1 mL aliquot (0-24 h ) Serial dilution and nutrient agar plating Incubated for 24 h at 30 o C Plate count and plotting of Viable Cells/mL vs Time
Growth Curve ,[object Object],Viable cell count = Number of colonies * (1/Dilution) * (1/Volume)
Growth Curve – With NZVI ,[object Object],[object Object],[object Object]
Pseudomonas putida  F1 for TCE Degradation  ,[object Object],[object Object],[object Object],[object Object]
Pp  F1 for TCE Degradation  ,[object Object],Blank    P.  Pp  F1+TCE
NZVI in Growth Media ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],Blank   NZVI + TCE (in media)
Batch Experiments ,[object Object],[object Object],[object Object],[object Object],[object Object],Encapsulated NZVI  Encapsulated  P.putida  F1 TCE Solution  40 mL Vial
Re-dosing Experiments ,[object Object],Rotated  End-over-end for 3h Remove TCE  solution  Add new TCE  solution  Rotated  End-over-end 36 h  Aliquots  Analysis
Results ,[object Object],[object Object],Add new TCE Solution
NZVI Re-dosing ,[object Object]
Kinetic Studies ,[object Object]
Research Phase II- Summary ,[object Object],[object Object],[object Object]
Work Remaining TCE Degradation NZVI Bare Encapsulated Encapsulated NZVI Microorganisms Pp F1 D.  BAV1 Encapsulated Microorganisms Combined NZVI-microorganism system Research Phase III
Research Phase III Combined NZVI- D  BAV1 System
Research Phase III ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Dehalococcoides  BAV1 ,[object Object],[object Object],[object Object],[object Object]
D .BAV1 growth Studies D. BAV1   incubated at 22±2  o  C in (MSM) media and shaken 1 mL aliquot  at  regular interval (0-36 h ) Serial dilution and nutrient agar plating Incubated for 24 h at 22±2  o C Plate count and plotting of Viable Cells/mL vs Time
D . BAV1 Encapsulation
TCE Degradation Batch Studies Combined metal-microorganism Encapsulated  D.BAV1 Encapsulated NZVI (re-dosed) Encapsulated NZVI
pH-ORP Data Acquisition System
pH-ORP Change ,[object Object],[object Object],[object Object],[object Object]
Kinetic Study
Research Phase III -Summary ,[object Object],[object Object],[object Object],[object Object]
Conclusions ,[object Object],[object Object],[object Object],[object Object],[object Object]
Future Directions ,[object Object],[object Object],[object Object],[object Object]
Acknowledgements ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
[object Object]

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Sharanya Presentation

  • 1. Alginate Encapsulated Nanoparticle-Microorganism System for Trichloroethylene Remediation
  • 2.
  • 4. Global Nano Market US$ in Billion (2015) Source: NSF
  • 5.
  • 6.
  • 7.
  • 8. NPs for Water Remediation Nanoparticles Contaminant Reference Nano Zeolites Toluene, nitrogen dioxide Song et al. (2004) Carbon nanotubes (CNTs) p-nitrophenol, benzene, toluene, heavy metal ions,dimethylbenzene Jin et al. (2007) Bimetallic nanoparticles (Pd/Fe) PCBs, chlorinated methane, ethene, Trichloroethylene (TCE) Xu and Bhattacharyya (2005) Xu and Zhao (2007) Wang and Zhang (1997) Kim et al. (2010) Ni/Fe and Pd/Au nanoparticles TCE and PCBs He and Zhao (2005) TiO 2 photocatalyst Heavy metal ions Pentachlorophenol (PCP) Pena et al. (2005) Quan et al. (2005) NZVI Herbicides (Alachlor) Thompson et al. (2010) NZVI Nitrate Bezbaruah et al. (2009) NZVI TCE Bezbaruah et al. (2011)
  • 9.
  • 10.
  • 11.
  • 12. In-situ Injection Injection Well Groundwater Flow TCE Contaminated plume NZVI Aquifer
  • 14.
  • 15.
  • 16.
  • 17.
  • 18. TCE Degradation Mechanism - NZVI C=C Cl Cl H Cl Fe 0 Cl - e - C=C H Cl H Cl Fe 0 Cl - e - C=C H Cl H H Fe 0 Cl - e - C=C H H H H TCE DCE VC Ethene
  • 19.
  • 21. P. putida F1 Interactions with NZVI Shabnam, 2011
  • 22. E. coli 8739 interactions with NZVI
  • 24. Experimental Design Microorganisms Pp F1 D. BAV1 Encapsulated Microorganisms Combined NZVI-Microorganism System TCE Degradation NZVI Bare Encapsulated Encapsulated NZVI Research Phase I
  • 25. Research Phase I Encapsulated NZVI System
  • 26.
  • 27.
  • 28.
  • 29.
  • 30. Preparation of Capsules a : Capsules 30 mg NZVI 1.33% Iron loss Bezbaruah et al., 2011 b b : Encapsulated NZVI 4 g Maltodextrin 6 mL DI water 0.25 g CaCl 2 50 mL alginate Peristaltic pump Stirrer 6 cm b a
  • 31.
  • 32.
  • 33.
  • 34.
  • 35. TCE Degradation Kinetics TCE degradation followed First Order Kinetics for both bare and encapsulated NZVI No significant difference Bare and Encapsulated NZVI (95% CI, Two Way ANOVA ) Bezbaruah et al., 2011 Batch Initial TCE concentration mg L -1 Reaction rate constant R 2 k obs 10 -2 min -1 k sa 10 -3 L m -2 min -1 Bare NZVI 1 2.92 1.6 0.9689 10 2.35 1.3 0.9801 30 1.53 0.8 0.9897 40 2.24 1.2 0.9868 Encapsulated NZVI 1 3.23 1.7 0.9832 10 2.45 1.3 0.9491 30 1.92 1.0 0.9921 40 2.21 1.2 0.9425
  • 36.
  • 37.
  • 38.
  • 39. Work Remaining Microorganisms Pp F1 D. BAV1 Encapsulated Microorganisms Combined NZVI-Microorganism system TCE Degradation NZVI Bare Encapsulated Encapsulated NZVI
  • 40. Experimental Design Microorganisms Pp F1 D. BAV1 Encapsulated Microorganisms Combined NZVI-Microorganism system TCE Degradation NZVI Bare Encapsulated Encapsulated NZVI Research Phase II
  • 42. TCE Degrading Bacteria Microorganism Method of Removal End Product Reference Pseudomonas putida F1 Direct Oxidation Co-metabolism ETH (Sun and Wood 1996); (Kim et al. 2010b); (Radway et al. 1998) Clostridium bifermentans DPH-120 Co-metabolism c-DCE (Chang et al. 2000) Dehalospirillum multivorans Direct Oxidation c-DCE (Neuman et al.1994) Dehalococcoides ethenogenes 195 Reductive dechlorination ETH (Maymo-Gatell et al. 1999), (Fennell et al. 2001) Dehalococcoides BAV1 Reductive dechlorination ETH (Krajmalnik-Brown et al. 2004; Maymo-Gatell et al. 1999),(He et al. 2003) Dehalococcoides VS Reductive dechlorination ETH (Cupples et al. 2003) Dehalococcoides FL2 Reductive dechlorination ETH (El Fantroussi et al. 1998)
  • 43.
  • 44. Research Phase II Combined NZVI- Pp F1 System
  • 45.
  • 46.
  • 47. Growth Curve- Pseudomonas putida F1 P. putida incubated at 30 o C in TSB media and shaken for 24 h 1 mL aliquot (0-24 h ) Serial dilution and nutrient agar plating Incubated for 24 h at 30 o C Plate count and plotting of Viable Cells/mL vs Time
  • 48.
  • 49.
  • 50.
  • 51.
  • 52.
  • 53.
  • 54.
  • 55.
  • 56.
  • 57.
  • 58.
  • 59. Work Remaining TCE Degradation NZVI Bare Encapsulated Encapsulated NZVI Microorganisms Pp F1 D. BAV1 Encapsulated Microorganisms Combined NZVI-microorganism system Research Phase III
  • 60. Research Phase III Combined NZVI- D BAV1 System
  • 61.
  • 62.
  • 63. D .BAV1 growth Studies D. BAV1 incubated at 22±2 o C in (MSM) media and shaken 1 mL aliquot at regular interval (0-36 h ) Serial dilution and nutrient agar plating Incubated for 24 h at 22±2 o C Plate count and plotting of Viable Cells/mL vs Time
  • 64. D . BAV1 Encapsulation
  • 65. TCE Degradation Batch Studies Combined metal-microorganism Encapsulated D.BAV1 Encapsulated NZVI (re-dosed) Encapsulated NZVI
  • 67.
  • 69.
  • 70.
  • 71.
  • 72.
  • 73.

Hinweis der Redaktion

  1. Zeolites are aluminosilicate materials commonly used as adsorbents
  2. Iron core shell --- oxidized--- electron donor (so lises e-) The organic compound is reduced
  3. aquifer is a wet underground layer of water-bearing permeable rock
  4. Each step Cl- is knocked out Benign product ---ethene
  5. 1.Borohydride is dropped into ferrous 2.Vaccum dried(figure a and b) 3. Agglomeration 4.XRD peak indicative of Fe0 not oxide!
  6. 2 factor: factor 1(2 treatments- – bare and encapsulated) Factor 2: (concentration) 4 concentrations –triplicates ---2 factors(bare and encapsulated) 24 experimental k values More interested in type of NZVI Difference in treatments means (k) difference in treatment means concentration!(same type of reaction) Ho- there is no difference in means of K Ha: there is a difference in means for Conc: p=o reject Ho for bare/encapsulated : p=0.211 accept ho alpha =0.05