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Microbial Application to Environment
Contribution of Microbes to Nutrient Cycling:
Microbes in Carbon Cycle;
Microbes play a critical role in carbon cycle on the global scale that is a
key constituent of all living organisms. Microorganisms avail carbon for
living organisms and for themselves as well through extracting it from
nonliving sources. In aquatic habitats, microbes convert carbon
anaerobically, present at oxygen-free zones such as deep mud of lakes
and ponds. Carbon dioxide (CO2) is the most common form of carbon
that enters a carbon cycle. CO2 is a water-soluble gas present in the
atmosphere. Plants and photosynthetic alga use CO2 during
photosynthesis to synthesize carbohydrates. Additionally,
chemoautotrophs such as archaea and bacteria also utilize CO2 to
synthesize sugars. This carbon, present in the form of sugar, is further
processed through a chain of reactions during respiration known as
tricarboxylic acid cycle resulting into energy. Microbes may also use
carbon under anaerobic conditions to produce energy through a process
called as fermentation.
Plants are the primary producers in a terrestrial ecosystem; however,
free-living planktons, cyanobacteria, and symbionts such as lichens also
contribute in fixing carbon in some ecosystems. Nonliving organic
material is recycled by heterotrophic bacteria and fungi, whereas
saprobes utilize organic material and produce CO2 during respiration,
thereby contributing to carbon cycle. However, higher animals, e.g.,
herbivores and carnivores, also digest organic materials to obtain energy
using gut microbiota residing in their intestinal tracts; the process is
known as decomposition, resulting into inorganic products such as CO2,
ammonia, and water.
Actinobacteria and Proteobacteria are capable of degrading soluble
organic compounds, e.g., organic acids, amino acids, and sugars.
Similarly, Bacteroidetes are also involved in degradation of more
recalcitrant carbon compounds, e.g., cellulose, lignin, and chitin, and
utilize higher level of available nitrogen that help in production of
extracellular and transport enzymes. On the contrary, bacteria living in
low-nitrogen environments are more able to metabolize nitrogen-rich
organic compounds, e.g., amino acids. The abundance of α-
Proteobacteria and Bacteroidetes favors carbon mineralization, whereas
Acidobacteriota oppose it
Microbes in Methane Production;
Some microbes execute anaerobic or fermentative degradation of
organic compounds into organic acids and some gases, e.g., hydrogen
and CO2. Methanogens can use that hydrogen to reduce CO2 into
methane under strict anaerobic conditions. To complete cycle, methane-
oxidizing bacteria, e.g., methanotrophs, transform methane to CO2,
water, and energy under aerobic conditions.
Other microbes such as green and purple sulfur bacteria participate in
carbon cycle by degrading hydrogen sulfide (H2S) into compounds
having carbon during energy production (see in reaction). Some bacteria,
e.g., Thiobacillus ferrooxidans, derive energy from oxidation of ferrous
iron to ferric iron and thereby contribute to carbon cycle. Few microbes
such as Bacteroides succinogenes, Clostridium butyricum, and
Syntrophomonas spp. make a collaborative effort (also known as
interspecies hydrogen transfer) for anaerobic degradation of carbon to
produce CO2 and methane in bulk. The following reaction shows
anaerobic photoautotrophism in purple sulfur bacteria:
2CO2+H2S+2H2O→2(CH2O) +H2SO4
Microbes in Nitrogen Cycle;
Nitrogen is an essential element present in protein and nucleic acid
structure. Microorganisms play a critical role in nitrogen cycle through
various processes such as nitrogen fixation, nitrate reduction,
nitrification, denitrification, etc. The microbial processes limit the
productivity of an ecosystem because nitrogen availability is a limiting
factor for plant biomass production. Ammonification involves
decomposition of organic nitrogen into ammonia. Both bacteria and
archaea can fix atmospheric nitrogen through reduction into ammonium
Nitrogenase is an oxygen-sensitive enzyme that catalyzes nitrogen
fixation under low oxygen environment. N-fixation requires energy in
form of ATP (16 mol) per
mole of fixed nitrogen.
N2+8H++8e−+16ATP=2NH3+H2+16ADP+16Pi
The free-living microbes such as Azotobacter, Burkholderia, and
Clostridium have an ability to fix nitrogen, and few of them form a
symbiotic relationship with the rhizosphere of plants such as Rhizobium,
Mesorhizobium, and Frankia. Sophora and Clianthus are native legumes
and form a symbiotic relationship with Mesorhizobium or Rhizobium
leguminosarum. The symbiotic rhizobia can fix nitrogen by two or three
orders of magnitude higher than free-living soil bacteria.
Nitrification involves two steps: first, ammonia is oxidized to nitrite and
then to nitrate. The oxidation of ammonia to nitrite is carried out by few
soil bacteria, e.g., Nitrosospira, Nitrosomonas, Crenarchaeum, or
Nitrososphaera, and thereafter nitrite is oxidized to nitrate by some
bacteria, e.g., Nitrobacter and Nitrospira Nitrification also changes the
ionic state of soil from positive to negative through oxidation of
ammonia to nitrite and release of energy, which is used by nitrifying
microbes to assimilate CO2.
Denitrification involves sequential reduction of nitrate (NO3 −), nitrite
(NO2 −), and nitric oxide (NO) to the greenhouse gas nitrous oxide
(N2O) or benign nitrogen gas (N2). Since this process requires limiting
oxygen, therefore, it occurs mostly in waterlogged areas that provide
anaerobic environment. Nitrogen cycle involves denitrification process
through which fixed nitrogen returns to the atmosphere from soil and
water in order to complete the nitrogen cycle. Denitrification involves a
range of soil microbiota belonging to Proteobacteria, Actinobacteria, and
Firmicutes and other soil eukaryotes. Most of the bacteria lack single or
multiple enzymes involved in denitrification and known to be
incomplete denitrifier, for example, most of the fungi and bacteria lack
nitrous oxide reductase and thereby produce N2O as a final product.
Therefore, incomplete denitrification results into emission of greenhouse
gases.
Microbes in Sulfur Cycle;
Sulfur is an important component of a couple of vitamins and essential
metabolites, and it is found in two amino acids, cysteine, and
methionine. Despite its paucity in cells, it is an 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 involves some unique groups of
prokaryotes. Two unrelated groups of prokaryotes 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→SO4lithoorphototrophicsulfuroxidation
Sulfur-oxidizing prokaryotes 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, because 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.
Microbes in Phosphorus Cycle;
Phosphorus is a critical element of various building blocks such as
nucleic acids, e.g., DNA and RNA, ADP, ATP, and phospholipids.
Phosphorus is a rare element in the environment because of its tendency
to precipitate in the presence of divalent and trivalent cations at neutral
and alkaline ph.
Microorganisms (bacteria and fungi) mineralize organic phosphate in the
form of phosphate esters into inorganic phosphate through a process
driven by phosphatase enzymes. Additionally, they also convert
insoluble phosphorus into soluble form by a reaction with resulting
byproducts such as organic acids. Mycorrhizal fungi help plants to
overcome phosphorus limitation through its mobilization from insoluble
mineral form by producing oxalate, e.g., various ectomycorrhizal
basidiomycetous fungi express phosphate transporters in their
extraradical hyphae during phosphorus deficiency in surrounding
environments.

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Environmental Microbes.docx

  • 1. Microbial Application to Environment Contribution of Microbes to Nutrient Cycling: Microbes in Carbon Cycle; Microbes play a critical role in carbon cycle on the global scale that is a key constituent of all living organisms. Microorganisms avail carbon for living organisms and for themselves as well through extracting it from nonliving sources. In aquatic habitats, microbes convert carbon anaerobically, present at oxygen-free zones such as deep mud of lakes and ponds. Carbon dioxide (CO2) is the most common form of carbon that enters a carbon cycle. CO2 is a water-soluble gas present in the atmosphere. Plants and photosynthetic alga use CO2 during photosynthesis to synthesize carbohydrates. Additionally, chemoautotrophs such as archaea and bacteria also utilize CO2 to synthesize sugars. This carbon, present in the form of sugar, is further processed through a chain of reactions during respiration known as tricarboxylic acid cycle resulting into energy. Microbes may also use carbon under anaerobic conditions to produce energy through a process called as fermentation.
  • 2. Plants are the primary producers in a terrestrial ecosystem; however, free-living planktons, cyanobacteria, and symbionts such as lichens also contribute in fixing carbon in some ecosystems. Nonliving organic material is recycled by heterotrophic bacteria and fungi, whereas saprobes utilize organic material and produce CO2 during respiration, thereby contributing to carbon cycle. However, higher animals, e.g., herbivores and carnivores, also digest organic materials to obtain energy using gut microbiota residing in their intestinal tracts; the process is known as decomposition, resulting into inorganic products such as CO2, ammonia, and water. Actinobacteria and Proteobacteria are capable of degrading soluble organic compounds, e.g., organic acids, amino acids, and sugars. Similarly, Bacteroidetes are also involved in degradation of more recalcitrant carbon compounds, e.g., cellulose, lignin, and chitin, and utilize higher level of available nitrogen that help in production of extracellular and transport enzymes. On the contrary, bacteria living in low-nitrogen environments are more able to metabolize nitrogen-rich organic compounds, e.g., amino acids. The abundance of α- Proteobacteria and Bacteroidetes favors carbon mineralization, whereas Acidobacteriota oppose it Microbes in Methane Production; Some microbes execute anaerobic or fermentative degradation of organic compounds into organic acids and some gases, e.g., hydrogen and CO2. Methanogens can use that hydrogen to reduce CO2 into methane under strict anaerobic conditions. To complete cycle, methane- oxidizing bacteria, e.g., methanotrophs, transform methane to CO2, water, and energy under aerobic conditions.
  • 3. Other microbes such as green and purple sulfur bacteria participate in carbon cycle by degrading hydrogen sulfide (H2S) into compounds having carbon during energy production (see in reaction). Some bacteria, e.g., Thiobacillus ferrooxidans, derive energy from oxidation of ferrous iron to ferric iron and thereby contribute to carbon cycle. Few microbes such as Bacteroides succinogenes, Clostridium butyricum, and Syntrophomonas spp. make a collaborative effort (also known as interspecies hydrogen transfer) for anaerobic degradation of carbon to produce CO2 and methane in bulk. The following reaction shows anaerobic photoautotrophism in purple sulfur bacteria: 2CO2+H2S+2H2O→2(CH2O) +H2SO4 Microbes in Nitrogen Cycle;
  • 4. Nitrogen is an essential element present in protein and nucleic acid structure. Microorganisms play a critical role in nitrogen cycle through various processes such as nitrogen fixation, nitrate reduction, nitrification, denitrification, etc. The microbial processes limit the productivity of an ecosystem because nitrogen availability is a limiting factor for plant biomass production. Ammonification involves decomposition of organic nitrogen into ammonia. Both bacteria and archaea can fix atmospheric nitrogen through reduction into ammonium Nitrogenase is an oxygen-sensitive enzyme that catalyzes nitrogen fixation under low oxygen environment. N-fixation requires energy in form of ATP (16 mol) per mole of fixed nitrogen. N2+8H++8e−+16ATP=2NH3+H2+16ADP+16Pi The free-living microbes such as Azotobacter, Burkholderia, and Clostridium have an ability to fix nitrogen, and few of them form a symbiotic relationship with the rhizosphere of plants such as Rhizobium, Mesorhizobium, and Frankia. Sophora and Clianthus are native legumes
  • 5. and form a symbiotic relationship with Mesorhizobium or Rhizobium leguminosarum. The symbiotic rhizobia can fix nitrogen by two or three orders of magnitude higher than free-living soil bacteria. Nitrification involves two steps: first, ammonia is oxidized to nitrite and then to nitrate. The oxidation of ammonia to nitrite is carried out by few soil bacteria, e.g., Nitrosospira, Nitrosomonas, Crenarchaeum, or Nitrososphaera, and thereafter nitrite is oxidized to nitrate by some bacteria, e.g., Nitrobacter and Nitrospira Nitrification also changes the ionic state of soil from positive to negative through oxidation of ammonia to nitrite and release of energy, which is used by nitrifying microbes to assimilate CO2. Denitrification involves sequential reduction of nitrate (NO3 −), nitrite (NO2 −), and nitric oxide (NO) to the greenhouse gas nitrous oxide (N2O) or benign nitrogen gas (N2). Since this process requires limiting oxygen, therefore, it occurs mostly in waterlogged areas that provide anaerobic environment. Nitrogen cycle involves denitrification process through which fixed nitrogen returns to the atmosphere from soil and water in order to complete the nitrogen cycle. Denitrification involves a range of soil microbiota belonging to Proteobacteria, Actinobacteria, and Firmicutes and other soil eukaryotes. Most of the bacteria lack single or multiple enzymes involved in denitrification and known to be incomplete denitrifier, for example, most of the fungi and bacteria lack nitrous oxide reductase and thereby produce N2O as a final product. Therefore, incomplete denitrification results into emission of greenhouse gases. Microbes in Sulfur Cycle;
  • 6. Sulfur is an important component of a couple of vitamins and essential metabolites, and it is found in two amino acids, cysteine, and methionine. Despite its paucity in cells, it is an 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 involves some unique groups of prokaryotes. Two unrelated groups of prokaryotes 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→SO4lithoorphototrophicsulfuroxidation Sulfur-oxidizing prokaryotes 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, because 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
  • 7. 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. Microbes in Phosphorus Cycle; Phosphorus is a critical element of various building blocks such as nucleic acids, e.g., DNA and RNA, ADP, ATP, and phospholipids. Phosphorus is a rare element in the environment because of its tendency to precipitate in the presence of divalent and trivalent cations at neutral and alkaline ph. Microorganisms (bacteria and fungi) mineralize organic phosphate in the form of phosphate esters into inorganic phosphate through a process driven by phosphatase enzymes. Additionally, they also convert insoluble phosphorus into soluble form by a reaction with resulting byproducts such as organic acids. Mycorrhizal fungi help plants to overcome phosphorus limitation through its mobilization from insoluble mineral form by producing oxalate, e.g., various ectomycorrhizal basidiomycetous fungi express phosphate transporters in their extraradical hyphae during phosphorus deficiency in surrounding environments.