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| The rise and success of secondary
red algae : |
This
project focused on the evolution and selection of a particular metalloenzyme
family, the superoxide dismutases (SOD), which utilize the redox
sensitive and thus biogeochemically significant metals Fe, Mn, Cu/Zn,
or Ni. I successfully showed that in the secondary red algae,
diatoms, historically high Mn measurements could be accounted for
by the protective role and constitutive expression of MnSODs in
the plastid. This was previously unknown to the field (Wolfe-Simon
et al., 2006). In addition, the importance of Mn to secondary
red algae also suggests a possible role for Mn in their ascent to
dominance of the marine system during the Mesozoic. Furthermore,
the Mn and FeSOD genes are related due to an ancient gene duplication
event. I reviewed (Wolfe-Simon
et al., 2005) and extended our understanding of the molecular
evolution and phylogenetic radiation of the Mn and FeSOD isoforms
in photoautotrophs by running detailed maximum likelihood and Bayesian
phylogenetic analyses (Wolfe-Simon
et al., in review). The eukaryotic subcellular
residence of the proteins today suggests that they were inherited
originally from the symbiont ancestor which led to the rise of the
modern eukaryotic organelles (Wolfe-Simon
et al. 2006).
[Collaborators:
...] |
| Proterozoic primary production
and trace metals: |
| Did
trace metal availability support the dominance of cyanobacteria
during a substantial amount of Earth's early history? Currently,
my data suggest that cyanobacteria have biological mechanisms to
cope with reduced Fe and reduced Cu conditions as compared to algae
and other photosynthetic eukaryotes (Wolfe-Simon et al., in prep).
Cyanobacteria dominated the oceans until approximately 0.5-0.8 billion
years ago (Ga) despite drastic environmental changes. Eukaryotic
photoautotrophs evolved during this time (2.7-1.5 Ga) but their
rise to ecological prominence and multicellularity was delayed.
Biochemical strategies to cope with changing metal availability
may have been critical. A major change in metal availability was
the decrease in ocean Fe after 1.8 Ga. This decrease would have
been accompanied by a decrease in Cu if the oceans became euxinic
(reduced and sulfur rich) at this time. Hence, I am investigating
differences in the ways that cyanobacteria and algae cope with Fe
and Cu stress. I found that the Cu quota of the cyanobacterium Synechocystis
PCC6803 does not increase under Fe-deficiency. This contrasts
with previous studies with eukaryotic photoautotrophs showing increased
use of Cu under Fe-deficiency. For cyanobacteria, production
of compensatory Cu proteins presumably involves reallocation of
intracellular Cu rather than increased Cu uptake. The implication
is that cyanobacteria were better equipped to cope with Fe ocean
redox changes at this time when Cu may have been scarce.
How did
the redox conditions of the environment, and thus micronutrient
availability, help drive the rise of algae?
As trace metal concentrations have varied over Earth history, a
major geochemical trend is the shift from abundantly soluble Fe
to Cu due to the affect of increased oxygen in the atmosphere over
geologic time (see above). There is evidence in the literature
that algae and other photosynthetic eukaryotes biochemically utilize
Cu in a stoichiometrically larger proportion than cyanobacteria.
I have tested the evolutionary validity of this hypothesis and shown
the increased cellular quota of Cu as well as the more economical
and efficient use of Cu in green algae when compared to cyanobacteria.
For example, green algae increase their expression of the PSI Cu
protein plastocyanin when under Fe-deficiency to replace the Fe-containing
protein cytochrome c6. Furthermore, they
modulate their expression of other Fe-rich PSI proteins including
PsaA and psaC. Another example relates back to my doctoral
work in that higher plants utilize CuZnSOD while more primitive
plants (including some early eukaryotic photoautotrophs) rely on
the constitutive expression of FeSOD. By combining controlled
laboratory experiments, biochemical analyses, and molecular genetic
modeling I will be able to forge a deeper understanding of historically
relevant events for the Proterozoic evolution of photosynthetic
life.
[Collaborators:
Ariel Anbar, Petra Fromme, Vim Vermaas]
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| Biological control on the stalled rise of oxygen: maybe cyanobacteria had an alternative, non-metal based, secret |
Maybe
metals aren't the only reason cyanobacteria continued to dominate
primary production during the sulfidic time of the Proterozoic.
Perhaps they also utilized the enzyme sulfide quinone reductase
to successfully fix carbon AND fix nitrogen all the while NOT produce
oxygen. Never underestimate the elegant flexibility of physiology.
Biology
does matter!
<<MORE
TO COME>>
[Collaborators:
Andy Knoll, David Johnston, Ann Pearson]
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| Fe-deficient primary production, zooplankton and the carbon cycle: |
<<COMING
SOON>>
[Collaborators:
Ariel Anbar, Jim Elser, Marcia Kyle]
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| Molybdenum and the nitrogen
cycle: |
Nitrogen
is vital for all known oxygenic photoautotrophs. The three main
pathways leading to nitrogen assimilation all require Mo. Nitrogenase
(Nif), responsible for the biological fixation of N2
gas to ammonia, is known to posses one atom of Mo per functional
subgroup. Nitrate reductase (NarB) also has one atom of Mo and reduced
nitrate to nitrite for further processing by the cell. MORE TO COME.
This project forms the basis for the PhD thesis of
Jennifer Glass. Jennifer is a PhD candidate working under the
guidance of Ariel
Anbar in the
School of Earth and Space Exploration
at Arizona State University. Jennifer
worked with me during my postdoctoral fellowship at ASU and continues
to be a close collaborator. For further information on this project,
please follow this link.
[Collaborators:
Jennifer Glass, Ariel Anbar] |
| Arsenic
and the origins of life: |
Arsenic
as a prebiotic chemical analog of phosphate (Wolfe-Simon
et al 2008). Essentially, Arsenic (in the oxidized 5+ state
as arsenate) is biologically, so similar to phosphate that many
enzymes cannot recognize the difference. This constitutes the basis
for much of the toxicity of arsenate and so most detoxification
pathways in biology aim to reduce arsenate to more volatile forms
for easier removal from biological systems. However, due to the
increased mobility of reduced arsenic species, often the toxicity
of arsenic increases as the redox state decreases.
Inorganically,
As and P have very similar atomic radii and electronegativity (especially,
compared to nitrogen which is directly above both on the periodic
table). In fact, in contrast to phosphorus, arsenic readily forms
sulfides and thus may have been available to early life at hydrothermal
vents and similar environments. Given the distinct similarity between
these two elements my coauthors and I assemble plausible TESTABLE
hypotheses regarding the liklihood of life arising to either originally
incorporate arsenate in a functional sense, and/or more speculatively,
alternative forms of life utilizing a genetic system entirely based
on arsenic. Check out our manuscript
and decide for yourself!
To
futher this hypothesis, we have embarked on two different approaches
to test assimilatory arsenic utilization. Firstly, we are collaborating
with Dr. Steve
Benner and Dr.
Nicole Leal at The Foundation
for Applied Molecular Evolution to measure the spontanous incorporation
of arsenate into a DNA backbone. In concert to this purely in
vitro approach, we are also examining arsenate-rich/phosphate-poor
environments to hunt and enrich cultures for organisms utilizing
arsenate in novel and unique modes.
[Collaborators:
Ariel Anbar, Steve Benner, Nicole Leal, Paul Davies, Dirk Schulze-Milch,
Ann Pearson.] |
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Many
people are curious how this work is done. How do we take living organisms
and peer deep in to the distant past? Here I explain some of our standard
techniques borrowed from disciplines spanning genomics to geochemistry.
To
explain how this work is done, I will describe one of the experiments
you might run. For example, to probe the nature of iron deficiency in
the cyanobactria Symechocystis sp. PCC6803. First, you need to:
1-
Grow the cells in batch cultures in defined media and measure parameters
like growth rate and chlorophyll concentrations. To do this, you will
innoculate a culture and then take samples to count the cells. Each day,
cell counts are done and might look a lot like this. Next, you will sample
a few milliliters of the culture, collect the cells out of the media,
and extract the chlorophyll a with Methanol (note, not all phytoplankton
work with Methanol). This sample is then measured on a spectrophotometer.
Once
you have characterized how cells grow under standard batch conditions,
its time to set up the chemostat. This is a
<<UNDER
CONSTRUCTION>>
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