Bacteria and Archaea and the Cycles of Elements in the Environment (page 4)
(This chapter has 4 pages)
© Kenneth Todar, PhD
The Sulfur Cycle
Sulfur is a component of a couple of vitamins and essential
metabolites
and it occurs in two amino acids, cysteine and methionine. In spite of
its paucity in cells, it is an absolutely essential element for living
systems. Like nitrogen and carbon, the microbes can transform sulfur
from
its most oxidized form (sulfate or SO4) to its most reduced
state (sulfide or H2S). The sulfur cycle, in particular,
involves
some unique groups of procaryotes and procaryotic processes. Two
unrelated
groups of procaryotes oxidize H2S to S and S to SO4.
The first is the anoxygenic photosynthetic purple and green sulfur
bacteria
that oxidize H2S as a source of electrons for cyclic
photophosphorylation.
The second is the "colorless sulfur bacteria" (now a misnomer because
the
group contains many Archaea) which oxidize H2S and S as
sources
of energy. In either case, the organisms can usually mediate the
complete
oxidation of H2S to SO4.
H2S----------------> S ----------------> SO4
litho
or phototrophic sulfur oxidation
Sulfur-oxidizing procaryotes are frequently thermophiles found in
hot
(volcanic) springs and near deep sea thermal vents that are rich in H2S.
They may be acidophiles, as well, since they acidify their own
environment
by the production of sulfuric acid.
Since SO4 and S may be used as electron acceptors for
respiration,
sulfate reducing bacteria produce H2S during a process of
anaerobic
respiration analogous to denitrification. The use of SO4 as
an electron acceptor is an obligatory process that takes place only in
anaerobic environments. The process results in the distinctive odor of
H2S in anaerobic bogs, soils and sediments where it occurs.
Sulfur is assimilated by bacteria and plants as SO4 for
use
and reduction to sulfide. Animals and bacteria can remove the sulfide
group
from proteins as a source of S during decomposition. These processes
complete
the sulfur cycle.

Figure 3. The Sulfur Cycle
The Phosphorus cycle
The phosphorus cycle is comparatively simple. Inorganic phosphate
exists
in only one form. It is interconverted from an inorganic to an organic
form
and back again, and there is no gaseous intermediate.
Phosphorus is an essential element in biological systems because it
is a constituent of nucleic acids, (DNA and RNA) and it occurs in the
phospholipids
of cell membranes. Phosphate is also a constituent of ADP and ATP which
are universally involved in energy exchange in biological systems.
Dissolved phosphate (PO4) inevitably ends up in the
oceans.
It is returned to land by shore animals and birds that feed on
phosphorus
containing sea creatures and then deposit their feces on land.
Dissolved
PO4 is also returned to land by a geological process, the
uplift
of ocean floors to form land masses, but the process is very slow.
However,
the figure below considers how PO4 is recycled among
land-based
groups of organisms.

Figure 4. The Phosphorus
Cycle.
Plants, algae and photosynthetic bacteria can absorb phosphate (PO4)
dissolved in water, or if it washes out of rocks and soils. They
incorporate
the PO4 into various organic forms, including such molecules
as DNA, RNA, ATP, and phospholipid. The plants are consumed by animals
wherein
the organic phosphate in the plant becomes organic phosphate in the
animal
and in the bacteria that live with the animal. Animal waste returns
inorganic
PO4 to the environment and also organic phosphate in the
form
of microbial cells. Dead plants and animals, as well as animal waste,
are
decomposed by microbes in the soil. The phosphate eventually is
mineralized
to the soluble PO4 form in water and soil, to be taken up
again
by photosynthetic organisms.
Ecology of a Stratified Lake
The role of microbes in the global cycle of elements (described
above)
can be visited on a smaller scale, in a lake, for example, like Lake
Mendota,
which may become stratified as illustrated in Figure 5. The surface of
the lake is well-lighted by the sun and is aerobic. The bottom of the
lake
and its sediments are dark and anaerobic. Generally there is less O2
and less light as the water column is penetrated from the surface.
Assuming
that the nutrient supply is stable and there is no mixing between
layers
of lake water, we should, for the time being, have a stable ecosystem
with
recycling of essential elements among the living systems. Here is how
it
would work.
At the surface, light and O2 are plentiful, CO2
is fixed and O2 is produced. Photosynthetic plants, algae
and
cyanobacteria produce O2, cyanobacteria can even fix N2;
aerobic bacteria, insects, animals and plants live here.
At the bottom of the lake and in the sediments, conditions are dark
and anaerobic. Fermentative bacteria produce fatty acids, H2
and CO2, which are used by methanogens to produce CH4.
Anaerobic respiring bacteria use NO3 and SO4 as
electron
acceptors, producing NH3 and H2S. Several soluble
gases are in the water: H2, CO2, CH4,
NH3 and H2S.
The biological activity at the surface of the lake and at the bottom
of the lake may have a lot to do with what will be going on in the
middle
of the water column, especially near the interface of the aerobic and
anaerobic
zones. This area, called the thermocline, is biologically very
active.
Bacterial photosynthesis, which is anaerobic, occurs here, using longer
wave lengths of light that will penetrate the water column and are not
absorbed by all the plant chlorophyll above. The methanotrophs will
stay
just within the aerobic area taking up the CH4 from the
sediments
as a carbon source, and returning it as CO2. Lithotrophic
nitrogen and sulfur utilizing bacteria do something analogous: they are
aerobes
that use NH3 and H2S from the sediments,
returning
them to NO3 and SO4.

Figure 5. Ecology of a
Stratified
lake
END OF CHAPTER
Return to Page 1
Previous Page | Textbook of Bacteriology Index