Impact of nanoscale zero valent iron on geochemistry and microbial populations in trichloroethylene contaminated aquifer materials.

Nanoscale zerovalent iron (NZVI) particles are a promising technology for reducing trichloroethylene (TCE) contamination in the subsurface. Prior to injecting large quantities of nanoparticles into the groundwater it is important to understand what impact the particles will have on the geochemistry and indigenous microbial communities. Microbial populations are important not only for nutrient cycling, but also for contaminant remediation and heavy metal immobilization. Microcosms were used to determine the effects of NZVI addition on three different aquifer materials from TCE contaminated sites in Alameda Point, CA, Mancelona, MI, and Parris Island, SC. The oxidation and reduction potential of the microcosms consistently decreased by more than 400 mV when NZVI was added at 1.5 g/L concentrations. Sulfate concentrations decreased in the two coastal aquifer materials, and methane was observed in the presence of NZVI in Alameda Point microcosms, but not in the other two materials. Denaturing gradient gel electrophoresis (DGGE) showed significant shifts in Eubacterial diversity just after the Fe(0) was exhausted, and quantitative polymerase chain reaction (qPCR) analyses showed increases of the dissimilatory sulfite reductase gene (dsrA) and Archaeal 16s rRNA genes, indicating that reducing conditions and hydrogen created by NZVI stimulate both sulfate reducer and methanogen populations. Adding NZVI had no deleterious effect on total bacterial abundance in the microcosms. NZVI with a biodegradable polyaspartate coating increased bacterial populations by an order of magnitude relative to controls. The lack of broad bactericidal effect, combined with the stimulatory effect of polyaspartate coatings, has positive implications for NZVI field applications.

[1]  Armand Masion,et al.  Relation between the redox state of iron-based nanoparticles and their cytotoxicity toward Escherichia coli. , 2008, Environmental science & technology.

[2]  G. Lowry,et al.  Effect of particle age (Fe0 content) and solution pH on NZVI reactivity: H2 evolution and TCE dechlorination. , 2006, Environmental science & technology.

[3]  Jizhong Zhou,et al.  Microbiological Characteristics in a Zero-Valent Iron Reactive Barrier , 2002, Environmental monitoring and assessment.

[4]  Paige J. Novak,et al.  Enhanced Dechlorination of Carbon Tetrachloride and Chloroform in the Presence of Elemental Iron and Methanosarcina barkeri, Methanosarcina thermophila, or Methanosaeta concillii , 1998 .

[5]  P. Alvarez,et al.  Utilization of Cathodic Hydrogen as Electron Donor for Chloroform Cometabolism by a Mixed, Methanogenic Culture , 1997 .

[6]  J. Vogan,et al.  Anaerobic corrosion reaction kinetics of nanosized iron. , 2008, Environmental science & technology.

[7]  Daniel W. Elliott,et al.  Applications of iron nanoparticles for groundwater remediation , 2006 .

[8]  T. Phelps,et al.  Biogeochemical dynamics in zero-valent iron columns: Implications for permeable reactive barriers , 1999 .

[9]  Bruno Dufour,et al.  Effect of adsorbed polyelectrolytes on nanoscale zero valent iron particle attachment to soil surface models. , 2009, Environmental science & technology.

[10]  Kelvin B. Gregory,et al.  Bioaugmentation of Fe(0) for the remediation of chlorinated aliphatic hydrocarbons. , 2000 .

[11]  A. Dahmke,et al.  Degradation of chlorinated ethylenes by Fe0: inhibition processes and mineral precipitation , 2002 .

[12]  B. Engelen,et al.  Methane and sulfate profiles within the subsurface of a tidal flat are reflected by the distribution of sulfate-reducing bacteria and methanogenic archaea. , 2007, FEMS microbiology ecology.

[13]  R. Tilton,et al.  Adsorbed polyelectrolyte coatings decrease Fe(0) nanoparticle reactivity with TCE in water: conceptual model and mechanisms. , 2009, Environmental science & technology.

[14]  Dongye Zhao,et al.  Preparation and characterization of a new class of starch-stabilized bimetallic nanoparticles for degradation of chlorinated hydrocarbons in water. , 2005, Environmental science & technology.

[15]  P. Alvarez,et al.  Assessment of anaerobic benzene degradation potential using 16S rRNA gene-targeted real-time PCR. , 2007, Environmental microbiology.

[16]  L. Liang,et al.  Geochemical and microbial reactions affecting the long-term performance of in situ ‘iron barriers’ , 2000 .

[17]  Pratim Biswas,et al.  Assessing the risks of manufactured nanomaterials. , 2006, Environmental science & technology.

[18]  E. Delong,et al.  Quantitative Analysis of Small-Subunit rRNA Genes in Mixed Microbial Populations via 5′-Nuclease Assays , 2000, Applied and Environmental Microbiology.

[19]  L. Daniels,et al.  Bacterial Methanogenesis and Growth from CO2 with Elemental Iron as the Sole Source of Electrons , 1987, Science.

[20]  R. Puls,et al.  Long‐Term Performance of Permeable Reactive Barriers Using Zero‐Valent Iron: Geochemical and Microbiological Effects , 2003, Ground water.

[21]  D. Sponza,et al.  Toxicity and treatability of carbontetrachloride and tetrachloroethylene in anaerobic batch cultures , 2003 .

[22]  D. Sholl,et al.  TCE dechlorination rates, pathways, and efficiency of nanoscale iron particles with different properties. , 2005, Environmental science & technology.

[23]  R. L. Valentine,et al.  Chemistry and Microbiology of Permeable Reactive Barriers for In Situ Groundwater Clean up , 2000 .

[24]  H. Heuer,et al.  Bacterial diversity of soils assessed by DGGE, T-RFLP and SSCP fingerprints of PCR-amplified 16S rRNA gene fragments: do the different methods provide similar results? , 2007, Journal of microbiological methods.

[25]  R. Sethi,et al.  Enhanced transport of zerovalent iron nanoparticles in saturated porous media by guar gum , 2009 .

[26]  B. Schink Fermentation of acetylene by an obligate anaerobe,Pelobacter acetylenicus sp. nov. , 1985, Archives of Microbiology.

[27]  D. Cha,et al.  Reductive dehalogenation of chlorinated ethenes with elemental iron: the role of microorganisms. , 2001, Water research.

[28]  A. Uitterlinden,et al.  Profiling of complex microbial populations by denaturing gradient gel electrophoresis analysis of polymerase chain reaction-amplified genes coding for 16S rRNA , 1993, Applied and environmental microbiology.

[29]  P. Alvarez,et al.  Microbial Characterization of Groundwater Undergoing Treatment with a Permeable Reactive Iron Barrier , 2007 .

[30]  R. Tilton,et al.  Fe0 nanoparticles remain mobile in porous media after aging due to slow desorption of polymeric surface modifiers. , 2009, Environmental science & technology.

[31]  A. Steinbüchel,et al.  Microbial degradation of poly(amino acid)s. , 2004, Biomacromolecules.

[32]  Kara L Nelson,et al.  Bactericidal effect of zero-valent iron nanoparticles on Escherichia coli. , 2008, Environmental science & technology.

[33]  V. de Lorenzo,et al.  Exploiting the genetic and biochemical capacities of bacteria for the remediation of heavy metal pollution. , 2002, FEMS microbiology reviews.

[34]  K. Jarrell,et al.  Nutritional requirements of the methanogenic archaebacteria , 1988 .

[35]  W. Verstraete,et al.  Effect of Phenylurea Herbicides on Soil Microbial Communities Estimated by Analysis of 16S rRNA Gene Fingerprints and Community-Level Physiological Profiles , 1999, Applied and Environmental Microbiology.

[36]  Bruno Dufour,et al.  Adsorbed triblock copolymers deliver reactive iron nanoparticles to the oil/water interface. , 2005, Nano letters.

[37]  Martin Stratmann,et al.  Iron corrosion by novel anaerobic microorganisms , 2004, Nature.

[38]  R. Oremland,et al.  Inhibition of methanogenesis in marine sediments by acetylene and ethylene: validity of the acetylene reduction assay for anaerobic microcosms. , 1975, Applied microbiology.

[39]  Pedro J J Alvarez,et al.  Adsorbed polymer and NOM limits adhesion and toxicity of nano scale zerovalent iron to E. coli. , 2010, Environmental science & technology.