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Chaudhary Sarwan Kumar Himachal Pradesh Krishi
Vishvavidyalaya
College of agriculture
Principles and Practices of Organic Farming
AGRON 513, (2+1)
Course instructor:
Dr Janardan Singh
Professor (Agronomy)
Presentation by:
Akarsh S G
A-2017-030-019
I year MSc (Agronomy)
NUTRIENT CYCLESNUTRIENT CYCLES
IN ECOSYSTEMSIN ECOSYSTEMS
NUTRIENT CYCLES: ECOSYSTEM TO ECOSPHERENUTRIENT CYCLES: ECOSYSTEM TO ECOSPHERE
 Nutrient cycling occurs at the local level
through the action of the biota.
 Nutrient cycling occurs at the global level
through geological processes, such as,
atmospheric circulation, erosion and
weathering.
NUTRIENT CYCLESNUTRIENT CYCLES
 The atoms of earth and life are the same; they just find themselves in different places
at different times.
 Most of the calcium in your bones came from cows, who got it from corn, which took
it from rocks that were once formed in the sea.
 The path atoms take from the living (biotic) to the non-living (abiotic) world and back
again is called a biogeochemical cycle.
Nutrients: The Elements of LifeNutrients: The Elements of Life
 Of the 50 to 70 atoms (elements)
that are found in living things, only 15
or so account for the major portion
of living biomass.
 Only around half of these 15 have
been studied extensively as they
travel through ecosystems or
circulate on a global scale.
Na SODIUM
M nMANGANESE
Fe IRON
C lCHLORINE
P PHOSPHORUS
AlALUMINUM
S SULFUR
M gMAGNESIUM
S iSILICON
K POTASSIUM
C a CALCIUM
N NITROGEN
H HYDROGEN
C CARBON
O OXYGEN
A GENERALIZED MODEL OF NUTRIENT CYCLING IN ANA GENERALIZED MODEL OF NUTRIENT CYCLING IN AN
ECOSYSTEMECOSYSTEM
 The cycling of nutrients in an ecosystem are interlinked by an a
number of processes that move atoms from and through organisms
and to and from the atmosphere, soil and/or rocks, and water.
 Nutrients can flow between these compartments along a variety of
pathways.
A GENERALIZED MODEL OF NUTRIENT CYCLING IN AN ECOSYSTEM
Nutrient Compartments in a TerrestrialNutrient Compartments in a Terrestrial
EcosystemEcosystem
 The organic compartment consists of the living organisms and their detritus.
 The available-nutrient compartment consists of nutrients held to surface of
soil particles or in solution.
 The third compartment consists of nutrients held in soils or rocks that are
unavailable to living organisms.
 The fourth compartment is the air which can be found in the atmosphere or in
the ground.
Uptake of Inorganic Nutrients from the SoilUptake of Inorganic Nutrients from the Soil
 With the exception of CO2 and O2 which enter
though leaves, the main path of all other
nutrients is from the soil through the roots of
producers.
 Even consumers which find Ca, P, S and other
elements in the water they drink, obtain the
majority of these nutrients either directly or
indirectly from producers.
The Atmosphere Is a Source of InorganicThe Atmosphere Is a Source of Inorganic
NutrientsNutrients
 The atmosphere acts as a reservoir for carbon dioxide (CO2), oxygen (O2) and water
(H2O).
 These inorganic compounds can be exchanged directly with the biota through the
processes of photosynthesis and respiration.
 The most abundant gas in the atmosphere is nitrogen (N2);about 80% by volume. Its
entry into and exit from the biota is through bacteria.
Some Processes By Which Nutrients AreSome Processes By Which Nutrients Are
RecycledRecycled
 Cycling within an ecosystem involves a
number of processes.
 These are best considered by focusing
attention on specific nutrients.
CARBON, HYDROGEN AND OXYGEN CYCLES INCARBON, HYDROGEN AND OXYGEN CYCLES IN
ECOSYSTEMSECOSYSTEMS
 C, H & O basic elements of life; making up from about 98% of plant biomass.
 CO2 and O2 enter biota from the atmosphere.
 Producers convert CO2 and H2O into carbohydrates (CH2O compounds) and
release O2 from water.
 Producers, consumers and decomposers convert CH2O compounds, using O2, back
into CO2 and H2O.
CARBON, HYDROGEN AND OXYGEN CYCLES IN ECOSYSTEMSCARBON, HYDROGEN AND OXYGEN CYCLES IN ECOSYSTEMS
 Carbon and oxygen cycle come out of the air as carbon dioxide during photosynthesis and are
returned during respiration.
 Oxygen is produced from water during photosynthesis and combines with the hydrogen to
form water during respiration.
NITROGEN CYCLE IN ECOSYSTEMSNITROGEN CYCLE IN ECOSYSTEMS
 Nitrogen (N2) makes up 78% of the atmosphere.
 Most living things, however, can not use atmospheric nitrogen to make
amino-acids and other nitrogen containing compounds.
 They are dependent on nitrogen fixing bacteria to convert N2 into NH3(NH4
+
).
Sources of Nitrogen to the SoilSources of Nitrogen to the Soil
 Natural ecosystems receive their
soil nitrogen through biological
fixation and atmospheric deposition.
 Agricultural ecosystems receive
additional nitrogen through fertilizer
addition.
Biological Sources of Soil NitrogenBiological Sources of Soil Nitrogen
 Only a few species of bacteria and
cyanobacteria are capable of
nitrogen fixation.
 Some are fee-living and others form
mutualistic associations with plants.
 A few are lichens.
Atmospheric Sources of Soil NitrogenAtmospheric Sources of Soil Nitrogen
 Lightning was the major source of soil nitrogen
until recent times when the burning of fossil
fuels became a major source of atmospheric
deposition.
 Nitrogen oxides come from a variety of
combustion sources that use fossil fuels.
◦ In urban areas, at least half of these pollutants
come cars and other vehicles.
Agricultural Supplements to Soil NitrogenAgricultural Supplements to Soil Nitrogen
 Various forms of commercial
fertilizer are added to agricultural
fields to supplement the nitrogen
lost through plant harvest.
 Crop rotation with legumes such as
soybeans or alfalfa is also practiced
to supplement soil nitrogen.
Biological Nitrogen FixationBiological Nitrogen Fixation
 Nitrogen fixation is the largest source of
soil nitrogen in natural ecosystems.
 Free-living soil bacteria and
cyanobacteria (blue-green “algae”) are
capable of converting N2 into ammonia
(NH3) and ammonium (NH4
+
).
 Symbiotic bacteria (Rhizobium) in the
nodules of legumes and certain other
plants can also fix nitrogen.
NitrificationNitrification
 Several species of bacteria can
convert ammonium (NH4
+
) into
nitrites (NO2
-
).
 Other bacterial species convert
nitrites (NO2
-
) to nitrates (NO3
-
).
Uptake of Nitrogen by PlantsUptake of Nitrogen by Plants
 Plants can take in either ammonium (NH4
+
) or
nitrates (NO3
-
) and make amino acids or nucleic
acids.
 These molecules are the building blocks of
proteins and DNA, RNA, ATP, NADP, respectively.
 These building blocks of life are passed on to
other trophic levels through consumption and
decomposition.
AmmonificationAmmonification
 Decomposers convert organic
nitrogen (CHON) into ammonia
(NH3) and ammonium (NH4
+
).
 A large number of species of
bacteria and fungi are capable of
converting organic molecules
into ammonia.
DenitrificationDenitrification
 A broad range of bacterial species
can convert nitrites, nitrates and
nitrous oxides into molecular
nitrogen (N2).
 They do this under anaerobic
conditions as a means of obtaining
oxygen (O2).
 Thus, the recycling of N is complete.
NITROGEN CYCLE IN ECOSYSTEMSNITROGEN CYCLE IN ECOSYSTEMS
 Molecular nitrogen in the air can be fixed into ammonia by a few species of
prokaryotes.
 Other bacterial species convert NH4
-
into NO2
-
and others to N03
-
.
 Producers can take up NH4
-
and to N03
-
use it to make CHON.
 Decomposers use CHON and produce NH4
-
.
 Recycling is complete when still other species convert N03
-
and NO2
-
into N2.
PHOSPHOROUS CYCLE IN ECOSYSTEMSPHOSPHOROUS CYCLE IN ECOSYSTEMS
 Phosphorus, as phosphate (PO4
-3
), is an essential element of life.
 It does not cycle through atmosphere, thus enters producers through the
soil and is cycled locally through producers, consumers and
decomposers.
 Generally, small local losses by leaching are balanced by gains from the
weathering of rocks.
 Over very long time periods (geological time) phosphorus follows a
sedimentary cycle.
Sulphur CycleSulphur Cycle
Plants can absorb directly the sulphur containing amino acids, e.g., cystine,
cysteine, and methionine but these amino acids fulfill only a small proportion or
requirements for sulphur.
To fulfill rest of the requirements of plants, sulphur passes through a cycle of
transformation mediated by microorganisms. It accumulates in the soil mainly as
a constituent of organic compounds and has to be converted to sulphates to
become readily available to the plants.
Sulphate-reducing bacteria have a key role in the sulphur cycle. They use sulphate
(SO42-) as a terminal electron acceptor in the degradation of organic matter, which
results in the production of hydrogen sulphide (H2S).
 Subsequently, the sulphide can be oxidized aerobically by chemolithotrophic
sulphur-oxidizing bacteria (for example, Thiobacillus or Beggiatoa spp.) or
anaerobically by phototrophic sulphur bacteria (for example, Chlorobium spp.) to
elemental sulphur (S°) and SO42-.
Sulphur transformations.Sulphur transformations.
Other transformations, which are carried out by specialized groups of
microorganisms, result in
•sulphur reduction (for example, Desulfuromonas spp.) and
• sulphur disproportionation (Desulfovibrio sulfodismutans).
 Organic sulphur compounds, such as dimethylsulphoxide (DMSO) can be
transformed into dimethylsulphide (DMS) and vice versa by several groups of
microorganisms. SH, sulfhydryl.
The sequential pattern of microbial degradation of complex organic matter in anoxic
environments in the presence and absence of sulphate.
Macromolecules, such as proteins, polysaccharides and lipids are hydrolysed by
hydrolytic bacteria. Subsequently, the monomers — amino acids, sugars and fatty
acids — are fermented by fermentative bacteria into a range of fermentation products,
such as acetate, propionate, butyrate, lactate and hydrogen.
In the presence of sulphate (a), sulphate-reducing bacteria consume these
fermentation products.
 However, in the absence of sulphate (b), hydrogen and acetate — the acetate having
been produced directly by fermentation or indirectly by acetogenesis — are consumed
by the methanogens.
GLOBAL NUTRIENT CYCLESGLOBAL NUTRIENT CYCLES
 The loss of nutrients from one ecosystem means a gain for another. (Remember the
law of conservation of matter.)
 When ecosystems become linked in this manor, attention shifts to a global scale. One
is now considering the ECOSPHERE or the whole of planet earth.
GLOBAL WATER CYCLEGLOBAL WATER CYCLE
 Oceans contain a little less than 98% of the earth’s water.
 Around 1.8% is ice; found in the two polar ice caps and mountain glaciers.
 Only 0.5% is found in the water table and ground water.
 The atmosphere contains only 0.001% of the earth’s water, but is the major
driver of weather.
GLOBAL WATER CYCLEGLOBAL WATER CYCLE
 Evaporation exceeds precipitation over the oceans; thus there is a net
movement of water to the land.
 Nearly 60% of the precipitation that falls on land is either evaporated or
transpired by plants; the remainder is runoff and ground water.
GLOBAL WATER CYCLEGLOBAL WATER CYCLE
GLOBAL CARBON CYCLEGLOBAL CARBON CYCLE
 All but a small portion of the earth’s carbon (C) is tied up in
sedimentary rocks; but the portion that circulates is what sustains
life.
 The active pool of carbon is estimated to be around 40,000 gigatons.
 Of active carbon, 93.2 % found in the ocean; 3.7% in soils; 1.7% in
atmosphere; 1.4% in vegetation.
GLOBAL CARBON CYCLEGLOBAL CARBON CYCLE
GLOBAL NITROGEN CYCLE IGLOBAL NITROGEN CYCLE I
 99.4% of exchangeable N is found
in the atmosphere; 0.5% is
dissolved in the ocean; 0.04% in
detritus ; 0.006% as inorganic N
sources; 0.0004% in living biota.
 Figure 54.19 in Freeman (2005)
gives major pathways and rates of
exchange.
GLOBAL NITROGEN CYCLE IIGLOBAL NITROGEN CYCLE II
 Humans are adding large amounts of N to ecosystems.
 Among the fossil fuel sources, power plants and automobiles are important
sources of atmospheric nitrogen deposition in the US.
 Investigations of native plant and natural ecosystem responses to nitrogen
deposition and global warming will be a focus of study.
 E.g. invasive species tend to be more devastating to ecosystems with high soil
nitrogen content
Reference :Reference :
 FUNDEMENTALS OF SOIL SCIENCE, Indian society of soil science ,revised edition
February 2012.
 THE USE OF NUTRIENTS IN CROPS PLANTS, N.K Fageria,CRC Press ,Taylor & francis
group.
 TEXT BOOK OF PLANT NUTRIENT MANAGEMENT, Indian society of Agronomy, New Delhi.
First edition Nov 2014
 Ghaly AE, Ramakrishnan VV (2015) Nitrogen Sources and Cycling in the Ecosystem and
its Role in Air, Water and Soil Pollution: A Critical Review. Journal of Pollution Effects &
Control  Cont 3(2): 136. doi:10.4172/2375-4397.1000136
 F.H Bormann and G.E Likens (1967) Nutrient cycling, science ,vol 155
 B. Mukherjee , D. Mukherjee, M. Nivedita (2008) Modelling carbon and nutrient cycling∗
in a simulated pond system at Ranchi ecological modeling 437-448
 Patrick Lavelle, Richard Dugdale, Robert Scholes, Ecosystems and Human Well-being:
Current State and Trends 333-351
 Muyzer G, Stams AJM (2008) The ecology and biotechnology of sulphate-reducing
bacteria. Nature Review, Microbiology 6: 441-454

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Nutrient cycling

  • 1. Chaudhary Sarwan Kumar Himachal Pradesh Krishi Vishvavidyalaya College of agriculture
  • 2. Principles and Practices of Organic Farming AGRON 513, (2+1) Course instructor: Dr Janardan Singh Professor (Agronomy) Presentation by: Akarsh S G A-2017-030-019 I year MSc (Agronomy)
  • 3. NUTRIENT CYCLESNUTRIENT CYCLES IN ECOSYSTEMSIN ECOSYSTEMS
  • 4. NUTRIENT CYCLES: ECOSYSTEM TO ECOSPHERENUTRIENT CYCLES: ECOSYSTEM TO ECOSPHERE  Nutrient cycling occurs at the local level through the action of the biota.  Nutrient cycling occurs at the global level through geological processes, such as, atmospheric circulation, erosion and weathering.
  • 5. NUTRIENT CYCLESNUTRIENT CYCLES  The atoms of earth and life are the same; they just find themselves in different places at different times.  Most of the calcium in your bones came from cows, who got it from corn, which took it from rocks that were once formed in the sea.  The path atoms take from the living (biotic) to the non-living (abiotic) world and back again is called a biogeochemical cycle.
  • 6. Nutrients: The Elements of LifeNutrients: The Elements of Life  Of the 50 to 70 atoms (elements) that are found in living things, only 15 or so account for the major portion of living biomass.  Only around half of these 15 have been studied extensively as they travel through ecosystems or circulate on a global scale. Na SODIUM M nMANGANESE Fe IRON C lCHLORINE P PHOSPHORUS AlALUMINUM S SULFUR M gMAGNESIUM S iSILICON K POTASSIUM C a CALCIUM N NITROGEN H HYDROGEN C CARBON O OXYGEN
  • 7. A GENERALIZED MODEL OF NUTRIENT CYCLING IN ANA GENERALIZED MODEL OF NUTRIENT CYCLING IN AN ECOSYSTEMECOSYSTEM  The cycling of nutrients in an ecosystem are interlinked by an a number of processes that move atoms from and through organisms and to and from the atmosphere, soil and/or rocks, and water.  Nutrients can flow between these compartments along a variety of pathways.
  • 8. A GENERALIZED MODEL OF NUTRIENT CYCLING IN AN ECOSYSTEM
  • 9. Nutrient Compartments in a TerrestrialNutrient Compartments in a Terrestrial EcosystemEcosystem  The organic compartment consists of the living organisms and their detritus.  The available-nutrient compartment consists of nutrients held to surface of soil particles or in solution.  The third compartment consists of nutrients held in soils or rocks that are unavailable to living organisms.  The fourth compartment is the air which can be found in the atmosphere or in the ground.
  • 10. Uptake of Inorganic Nutrients from the SoilUptake of Inorganic Nutrients from the Soil  With the exception of CO2 and O2 which enter though leaves, the main path of all other nutrients is from the soil through the roots of producers.  Even consumers which find Ca, P, S and other elements in the water they drink, obtain the majority of these nutrients either directly or indirectly from producers.
  • 11. The Atmosphere Is a Source of InorganicThe Atmosphere Is a Source of Inorganic NutrientsNutrients  The atmosphere acts as a reservoir for carbon dioxide (CO2), oxygen (O2) and water (H2O).  These inorganic compounds can be exchanged directly with the biota through the processes of photosynthesis and respiration.  The most abundant gas in the atmosphere is nitrogen (N2);about 80% by volume. Its entry into and exit from the biota is through bacteria.
  • 12. Some Processes By Which Nutrients AreSome Processes By Which Nutrients Are RecycledRecycled  Cycling within an ecosystem involves a number of processes.  These are best considered by focusing attention on specific nutrients.
  • 13. CARBON, HYDROGEN AND OXYGEN CYCLES INCARBON, HYDROGEN AND OXYGEN CYCLES IN ECOSYSTEMSECOSYSTEMS  C, H & O basic elements of life; making up from about 98% of plant biomass.  CO2 and O2 enter biota from the atmosphere.  Producers convert CO2 and H2O into carbohydrates (CH2O compounds) and release O2 from water.  Producers, consumers and decomposers convert CH2O compounds, using O2, back into CO2 and H2O.
  • 14. CARBON, HYDROGEN AND OXYGEN CYCLES IN ECOSYSTEMSCARBON, HYDROGEN AND OXYGEN CYCLES IN ECOSYSTEMS  Carbon and oxygen cycle come out of the air as carbon dioxide during photosynthesis and are returned during respiration.  Oxygen is produced from water during photosynthesis and combines with the hydrogen to form water during respiration.
  • 15. NITROGEN CYCLE IN ECOSYSTEMSNITROGEN CYCLE IN ECOSYSTEMS  Nitrogen (N2) makes up 78% of the atmosphere.  Most living things, however, can not use atmospheric nitrogen to make amino-acids and other nitrogen containing compounds.  They are dependent on nitrogen fixing bacteria to convert N2 into NH3(NH4 + ).
  • 16. Sources of Nitrogen to the SoilSources of Nitrogen to the Soil  Natural ecosystems receive their soil nitrogen through biological fixation and atmospheric deposition.  Agricultural ecosystems receive additional nitrogen through fertilizer addition.
  • 17. Biological Sources of Soil NitrogenBiological Sources of Soil Nitrogen  Only a few species of bacteria and cyanobacteria are capable of nitrogen fixation.  Some are fee-living and others form mutualistic associations with plants.  A few are lichens.
  • 18. Atmospheric Sources of Soil NitrogenAtmospheric Sources of Soil Nitrogen  Lightning was the major source of soil nitrogen until recent times when the burning of fossil fuels became a major source of atmospheric deposition.  Nitrogen oxides come from a variety of combustion sources that use fossil fuels. ◦ In urban areas, at least half of these pollutants come cars and other vehicles.
  • 19. Agricultural Supplements to Soil NitrogenAgricultural Supplements to Soil Nitrogen  Various forms of commercial fertilizer are added to agricultural fields to supplement the nitrogen lost through plant harvest.  Crop rotation with legumes such as soybeans or alfalfa is also practiced to supplement soil nitrogen.
  • 20. Biological Nitrogen FixationBiological Nitrogen Fixation  Nitrogen fixation is the largest source of soil nitrogen in natural ecosystems.  Free-living soil bacteria and cyanobacteria (blue-green “algae”) are capable of converting N2 into ammonia (NH3) and ammonium (NH4 + ).  Symbiotic bacteria (Rhizobium) in the nodules of legumes and certain other plants can also fix nitrogen.
  • 21. NitrificationNitrification  Several species of bacteria can convert ammonium (NH4 + ) into nitrites (NO2 - ).  Other bacterial species convert nitrites (NO2 - ) to nitrates (NO3 - ).
  • 22. Uptake of Nitrogen by PlantsUptake of Nitrogen by Plants  Plants can take in either ammonium (NH4 + ) or nitrates (NO3 - ) and make amino acids or nucleic acids.  These molecules are the building blocks of proteins and DNA, RNA, ATP, NADP, respectively.  These building blocks of life are passed on to other trophic levels through consumption and decomposition.
  • 23. AmmonificationAmmonification  Decomposers convert organic nitrogen (CHON) into ammonia (NH3) and ammonium (NH4 + ).  A large number of species of bacteria and fungi are capable of converting organic molecules into ammonia.
  • 24. DenitrificationDenitrification  A broad range of bacterial species can convert nitrites, nitrates and nitrous oxides into molecular nitrogen (N2).  They do this under anaerobic conditions as a means of obtaining oxygen (O2).  Thus, the recycling of N is complete.
  • 25. NITROGEN CYCLE IN ECOSYSTEMSNITROGEN CYCLE IN ECOSYSTEMS  Molecular nitrogen in the air can be fixed into ammonia by a few species of prokaryotes.  Other bacterial species convert NH4 - into NO2 - and others to N03 - .  Producers can take up NH4 - and to N03 - use it to make CHON.  Decomposers use CHON and produce NH4 - .  Recycling is complete when still other species convert N03 - and NO2 - into N2.
  • 26. PHOSPHOROUS CYCLE IN ECOSYSTEMSPHOSPHOROUS CYCLE IN ECOSYSTEMS
  • 27.  Phosphorus, as phosphate (PO4 -3 ), is an essential element of life.  It does not cycle through atmosphere, thus enters producers through the soil and is cycled locally through producers, consumers and decomposers.  Generally, small local losses by leaching are balanced by gains from the weathering of rocks.  Over very long time periods (geological time) phosphorus follows a sedimentary cycle.
  • 28. Sulphur CycleSulphur Cycle Plants can absorb directly the sulphur containing amino acids, e.g., cystine, cysteine, and methionine but these amino acids fulfill only a small proportion or requirements for sulphur. To fulfill rest of the requirements of plants, sulphur passes through a cycle of transformation mediated by microorganisms. It accumulates in the soil mainly as a constituent of organic compounds and has to be converted to sulphates to become readily available to the plants.
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  • 31. Sulphate-reducing bacteria have a key role in the sulphur cycle. They use sulphate (SO42-) as a terminal electron acceptor in the degradation of organic matter, which results in the production of hydrogen sulphide (H2S).  Subsequently, the sulphide can be oxidized aerobically by chemolithotrophic sulphur-oxidizing bacteria (for example, Thiobacillus or Beggiatoa spp.) or anaerobically by phototrophic sulphur bacteria (for example, Chlorobium spp.) to elemental sulphur (S°) and SO42-. Sulphur transformations.Sulphur transformations.
  • 32. Other transformations, which are carried out by specialized groups of microorganisms, result in •sulphur reduction (for example, Desulfuromonas spp.) and • sulphur disproportionation (Desulfovibrio sulfodismutans).  Organic sulphur compounds, such as dimethylsulphoxide (DMSO) can be transformed into dimethylsulphide (DMS) and vice versa by several groups of microorganisms. SH, sulfhydryl.
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  • 34. The sequential pattern of microbial degradation of complex organic matter in anoxic environments in the presence and absence of sulphate. Macromolecules, such as proteins, polysaccharides and lipids are hydrolysed by hydrolytic bacteria. Subsequently, the monomers — amino acids, sugars and fatty acids — are fermented by fermentative bacteria into a range of fermentation products, such as acetate, propionate, butyrate, lactate and hydrogen. In the presence of sulphate (a), sulphate-reducing bacteria consume these fermentation products.  However, in the absence of sulphate (b), hydrogen and acetate — the acetate having been produced directly by fermentation or indirectly by acetogenesis — are consumed by the methanogens.
  • 35. GLOBAL NUTRIENT CYCLESGLOBAL NUTRIENT CYCLES  The loss of nutrients from one ecosystem means a gain for another. (Remember the law of conservation of matter.)  When ecosystems become linked in this manor, attention shifts to a global scale. One is now considering the ECOSPHERE or the whole of planet earth.
  • 36. GLOBAL WATER CYCLEGLOBAL WATER CYCLE  Oceans contain a little less than 98% of the earth’s water.  Around 1.8% is ice; found in the two polar ice caps and mountain glaciers.  Only 0.5% is found in the water table and ground water.  The atmosphere contains only 0.001% of the earth’s water, but is the major driver of weather.
  • 37. GLOBAL WATER CYCLEGLOBAL WATER CYCLE  Evaporation exceeds precipitation over the oceans; thus there is a net movement of water to the land.  Nearly 60% of the precipitation that falls on land is either evaporated or transpired by plants; the remainder is runoff and ground water.
  • 39. GLOBAL CARBON CYCLEGLOBAL CARBON CYCLE  All but a small portion of the earth’s carbon (C) is tied up in sedimentary rocks; but the portion that circulates is what sustains life.  The active pool of carbon is estimated to be around 40,000 gigatons.  Of active carbon, 93.2 % found in the ocean; 3.7% in soils; 1.7% in atmosphere; 1.4% in vegetation.
  • 41. GLOBAL NITROGEN CYCLE IGLOBAL NITROGEN CYCLE I  99.4% of exchangeable N is found in the atmosphere; 0.5% is dissolved in the ocean; 0.04% in detritus ; 0.006% as inorganic N sources; 0.0004% in living biota.  Figure 54.19 in Freeman (2005) gives major pathways and rates of exchange.
  • 42. GLOBAL NITROGEN CYCLE IIGLOBAL NITROGEN CYCLE II  Humans are adding large amounts of N to ecosystems.  Among the fossil fuel sources, power plants and automobiles are important sources of atmospheric nitrogen deposition in the US.  Investigations of native plant and natural ecosystem responses to nitrogen deposition and global warming will be a focus of study.  E.g. invasive species tend to be more devastating to ecosystems with high soil nitrogen content
  • 43. Reference :Reference :  FUNDEMENTALS OF SOIL SCIENCE, Indian society of soil science ,revised edition February 2012.  THE USE OF NUTRIENTS IN CROPS PLANTS, N.K Fageria,CRC Press ,Taylor & francis group.  TEXT BOOK OF PLANT NUTRIENT MANAGEMENT, Indian society of Agronomy, New Delhi. First edition Nov 2014  Ghaly AE, Ramakrishnan VV (2015) Nitrogen Sources and Cycling in the Ecosystem and its Role in Air, Water and Soil Pollution: A Critical Review. Journal of Pollution Effects & Control  Cont 3(2): 136. doi:10.4172/2375-4397.1000136  F.H Bormann and G.E Likens (1967) Nutrient cycling, science ,vol 155  B. Mukherjee , D. Mukherjee, M. Nivedita (2008) Modelling carbon and nutrient cycling∗ in a simulated pond system at Ranchi ecological modeling 437-448  Patrick Lavelle, Richard Dugdale, Robert Scholes, Ecosystems and Human Well-being: Current State and Trends 333-351  Muyzer G, Stams AJM (2008) The ecology and biotechnology of sulphate-reducing bacteria. Nature Review, Microbiology 6: 441-454