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Title: Interactions of Chemosynthetic Bacteria with Mercury at Deepsea Hydrothermal Vents


1
Interactions of Chemosynthetic Bacteria with
Mercury at Deep-sea Hydrothermal Vents Melitza
Crespo-Medina1, Nicolas Bloom2, Aspassia
Chatziefthimiou1, John Reinfelder1, Costantino
Vetriani1 and Tamar Barkay1 1Cook College,
Rutgers University, New Brunswick, NJ, 2Studio
GeoChimica, Seattle, WA
ABSTRACT Microorganisms in geothermal
environments, such as deep-sea hydrothermal
vents, have likely evolved in presence of
elevated concentrations of mercury. Because this
mercury is likely complexed with sulfur,
chemolithoautotrophic microbes, that use reduced
sulfur and iron as a energy source are likely
exposed to the toxicity of mercury. To test this
hypothesis we collected water for chemical and
microbiological analyses at different distances
from diffuse flow vents at 9 ºN on the East
Pacific Rise (EPR), during oceanographic
expeditions in 2004 and 2005. Total mercury (THg)
concentrations in the 2004 samples ranged from
2.8 to 88.7 ng/L (methylmercury concentration 0.3 ng/L). Growth medium, designed to enrich for
chemolithoautotrophic thiosulfate oxidizing
microorganisms, was used to enumerate total and
mercury resistant (10 µM) microbes by the MPN
method. Mercury speciation in this medium,
determined with MINEQL (Version 4.5), showed the
exclusive presence of negatively charges -2
(61.3) and -4 (38.7) complexes of mercury
thiosulfate.  The bioavailability of these
complexes to microorganisms was determined using
mer-lux bio-reporters, which emit light as
mercury enters the cell. Results suggested an
enhanced bioavailability of mercury-thiosulfate
relative to mercuric-nitrate complexes. The
abundance of mercury resistant microbes was 6
and 13 of total thiosulfate oxidizing
chemolithoautotrophs in vent waters with THg
concentrations of 6.5 and 88.7 ng/L,
respectively. Thus, the number of resistant
microbes was directly related to the
concentration of THg in the water suggesting
acclimation of these microbes to life in the
presence of toxic mercury. Isolations from vent
water samples led to the identification of
mercury resistant bacteria belonging to several
genera, including, Thiomicrospira, Thioclava and
Halomonas whose mechanisms of mercury resistance
is currently being investigated. These initial
results begin to reveal the processes that
facilitate microbial life in metal rich
geothermal environment and will lead to an
understanding of the role of these microbes in
mercury biogeochemistry in these ecosystems.
MPN counts of chemosynthetic microbes in samples
collected on the EPR 9oN
RESULTS
Table 1. Selected chemical measurements of
diffuse flow waters from EPR 9ºN (Apr. 2004
expedition)
Table 3. Summary of MPN Results
1 MeHg concentration was
  • The percentage of resistant MPN counts was
    between 0.1 and 13.9
  • The highest resistant MPN counts was found in the
    sample with the highest mercury concentration
    • HgT concentrations varied and were not always
      related to temperature and sulfide

    Bioavailability of Hg(II) in medium 142-A
    Figure 5. 16S rRNA gene phylogeny of isolates
    from diffuse flow vents
    I. MINEQL modeling of 142-A 10 µM HgCl2
    Figure 2. Hg-thiosulfate speciation
    OBJECTIVE Study the interactions between mercury
    and chemosynthetic microorganisms isolated from
    deep-sea hydrothermal vents
    • All Hg(II) in 142-A with 10 µM HgCl2 was present
      as thiosulfate complexes, 61 as Hg(S2O3)2-2 and
      39 as Hg(S2O3)3-4
    • METHODS
    • Samples were collected on East the Pacific Rise
      9oN (Fig. 1), during DSV Alvin dives in April
      2004 and 2005. Samples were preserved on board of
      R/V Atlantis immediately upon retrieval
    • Samples from the 2004 cruise were analyzed for
      chemical compositions at Frontier GeoScience Inc.
      (Seattle, WA)
    • MINEQL Chemical Equilibrium Modeling System
      (Schecher et al., 1994), was used to determine
      mercury speciation in the growth (142-A) and the
      biosensor assay media
    • mer-lux biosensor assays were done according to
      Barkay et al., (1998)
    • The Most Probable Number (MPN) technique and
      growth medium 142-A were used to determine the
      number of chemosynthetic and chemosynthetic-mercur
      y (10 µM HgCl2) resistant bacteria. Total number
      of cells was determined by Acridine Orange Direct
      Counts.
    • 16S rDNA gene phylogeny was obtained using
      Clustal X and NJ analysis

    II. Hg speciation in the mer-lux biosensor assay
    media
    Table 2. The effect of increasing thiosulfate
    concentrations on the speciation of Hg(II), added
    as 10 nM Hg(NO3)2 to mer-lux biosensor assay
    medium
    mercury resistant strains
    • A merA PCR fragment from EPR84 was sequenced and
      found most closely related to the sequence of
      merA of Tn501 and Tn21
    • CONCLUSIONS
    • Hydrothermal fluids from diffuse flow vents are
      enriched in mercury with concentrations ranging
      from 2.8 to 88.7 ng/mL (Table 1)
    • Thiosulfate is the favored ligand of Hg in medium
      142-A, a growth medium formulated for
      chemolithoautotrophic marine bacteria (Fig. 2)
    • The use of the biosensor assay in conjunction
      with MINEQL speciation is a useful approach to
      determine bioavailability of Hg(II) under
      specific conditions (Table 2 and Fig. 3)
    • Thiosulfate reduces Hg(II) bioavailability, yet
      it does not abolish it
    • The bioavailability of Hg(II) decreases with the
      increased negative charge of the Hg-thiosulfate
      complex (Fig. 3)
    • In diffuse flow samples with higher mercury
      concentrations, the microbial community is likely
      to be adapted to the presence of mercury (Table
      3)
    • Chemosynthetic bacteria from diffuse flow
      environments are distributed among ? and ?-
      Proteobacteria four of the isolates were
      resistant to 10 µM HgCl2 (Fig. 4)
    • At 2 mM S2O3-2 Hg(II) speciation in mer-lux assay
      medium simulates that of 10 µM Hg(II) in 142-A
      growth medium

    III. Bioavailability of varied Hg-S2O3 species
    Figure 1. Study sites on the East Pacific Rise
    9ºN 50N/104 17W
    Figure 3. Induction of mer-lux decreased with
    increasing concentrations of S2O3-2
    LITERATURE CITED Barkay et al. 1998.
    Lux-facilitated detection of mercury in natural
    waters. in Bioluminescent Protocols, R. LaRossa
    (ed). Humana Press, Inc. Totowa, NJ.pp.
    231-246. Schecher et al. MINEQL A Chemical
    Equilibrium Program for Personal Computers
    Environmental Research Software Hallowell, ME,
    1994.
    • Induction of mer-lux decreased with S2O3-2 (A)
    • At 2 mM S2O3-2 bioavailability decreased about
      55 relative to assay media devoid of thiosulfate
      (B)
    • Bioavailability decreases in inverse proportion
      to an increase in the ratio of Hg(S2O3)3-4
      Hg(S2O3)-2 (B)

    Acknowledgements This work was supported by a
    National Science Foundation Graduate Research
    Fellowship to MCM and by an NSF Grant OCE
    03-27353 to C. Vetriani
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