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Chapter 5: Organisms and Organic Residues

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Title: Chapter 5: Organisms and Organic Residues


1
Chapter 5 Organisms and Organic Residues 51
Important Facts to Know
  • The importance of soil organisms and the roles
    they play in maintaining a sound productive
    environment.
  • The conditions favoring and potential impacts of
    non-beneficial organisms and their control.
  • The nature and composition of soil organic
    matter.
  • The role of soil organic matter in improving
    soil chemical physical properties.
  • The value and properties of manures, residues,
    domestic waste, and composts.

2
Homework Chapter 5

Questions 5, 8, 10, 13, and 15 _at_ 2pts 10
pts Due 14 October 2009
3
Kingdoms of Living Organisms
  • Animalia rodents, worms, insects
  • Plantae - plants
  • Fungi molds, mushrooms, mycorrhizae
  • Protista algae, protozoa, slime molds
  • Monera - bacteria, actinomycetes

4
52 Animalia Rodents, Worms Insects
  • A. Vertebrates (backbone)
  • Burrowing animals Moles, mice, shrews, gophers,
    rabbits, etc. (aeration, structure, fertility,
    plant damage)
  • Mix soil with burrowing
  • Hasten decomposition
  • Create macropores
  • Can have major effects on soils plants

5
B. Invertebrates (no backbone) 1.
Arthropods Organism Function Beetles
Primary consumer transport and mixing of
organics Ants Primary consumer transport and
mixing of organics movement of B horizon to
surface. Centipedes Predator minor role in soil
formation
6
  • 1. Arthropods (cont.)
  • Organism Function
  • Millipedes Saprophageous (feed on dead organic
    matter). Transport and mixing.
  • Springtails Primary consumer affect soil
    structure
  • Mites Saprophageous very important in
    numbers affect soil structure
  • 2. Gastropods Eat decaying vegetation (slugs,
    snails)

7
3. Annelids Organism Function Earthworm
(Lumbricidae spp.) most important component of
macrofauna (up to 80 of biomass). - Very
important in soil structure 1 order
breakdown -Sensitive to pH and moisture -Casts
are enriched in N and P major role in mixing
organic matter -2 million/ha in beech forest,
10 million/ha in pasture. None to few in acid
soils.
8
  • Lumbricidae terrestris
  • Originated in Europe
  • Uncommon in North America before European
    settlement.
  • Major effect upon forest floor and soil organic
    matter in North America, especially in riparian
    areas. Now considered a major problem in many
    ways, including native plants.

9
4. Nematodes Important as population regulators
and nutrient concentrators -Nearly microscopic
roundworms -Common in mull and grassland soils
some in forest soils -Can be parasites (roots)
or predators (on bacteria, fungi) -Fumigation
often improves tree growth may be due to
reduction of parasitic nematodes
10
53 Plantae (Plants)
  • Roots 30-40 of plant mass
  • Root hairs (single cell)
  • Rhizosphere zone within 1 mm chemically
    changed, high bacterial concentrations
  • Rhizosphere organisms decompose soil organic
    matter and mobilize nutrients from it

11
54 Fungi Molds, Mushrooms, Mycorrhizae
  • Many ways to classify
  • One useful way is into these two major groups
    based on how they get energy
  • Autotrophic Use sunlight inorganic chemical
    reactions for energy
  • Heterotrophic Use organic compounds for energy

12
Molds, Mushrooms, Yeast, Rusts
  • Heterotrophic
  • Tolerate low pH (most important in decomposition
    in acid forest soils because bacteria are
    acid-sensitive and do not perform well in acid
    systems)
  • Decomposers of OM
  • Mycorrhizae fungus root
  • - Symbiotic with plant roots
  • - essential to growth in many cases (e.g.,
    pines)
  • - aid in taking up water and nutrients
    (especially P), and they get carbohydrates in
    return

13
  • Two basic kinds of Mycorrhizae
  • Ectomycorrrhizae
  • Penetrate only outer cell layers of root and only
    intercellular spaces (Fig 5.4)
  • Form a sheath/mantle of mycelium on fine roots
    called Hartig Net
  • Common in trees (pines, spruces, larches, D. fir,
    oak, birches, beeches, hickory, cottonwood,
    eucalyptus, aspen)

14
  • 2. Endomycorrhizae
  • Penetrate host cells and change root morphology
    (monopodal, bifurcate, corroloid
  • Vesicular arbuscular mycorrhizae (form vesicles
    inside host cells - storage)
  • Occur in many plants including some trees

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17
55 Protista Algae, Protozoa Slime Molds
  • Protozoa
  • Consume decomposing organic matter, bacteria,
    and fungi
  • 1-celled organisms, motile (cilia or flagellum)
  • Cause of several human diseases (malaria,
    sleeping sickness, dysentery)

18
  • Algae
  • Carrry on photosynthesis (autotrophic)
  • Not decomposers
  • Green, blue-green (the latter now called
    cyanobacteria) fix N

19
56 Monera Bacteria Actinomycetes
  • Bacteria
  • Single-celled rod or spherical, 1-2 µm
  • 1 tsp 100,000,000 bacteria
  • Three subdivisions based on how they handle
    oxygen
  • Anaerobes Live only in the absence of O2
  • Facultative Can live in either the presence or
    absence of O2
  • Aerobes Live only in the presence of O2

20
  • Two major subdivisions based on how they get
    energy
  • Hetertrophs Live on dead organic matter
  • Autotrophs energy from sunlight or chemical
    reactions
  • Photoautotrophs use sunlight
  • Chemoautotrophs use inorganic chemical
    reactions

21
Some Important Chemoautotrophs
Nitrifying bacteria One of the most important
autorophic bacteria are nitrifying bacteria, who
convert ammonium (NH4) to nitrite (NO2-) and
nitrate (NO3-) 2NH4 3O2 --------gt 2NO2-
4H 2H2O Nitrosomonas 2NO2- O2 -------gt
2NO3- Nitrobacter
22
Very pH-sensitive (don't live below pH 5) Since
they produce acid, they are self-limiting.
However, nitrification has been observed in very
acidic forest soils. Nitrification in these
cases may be accomplished by heterotrophic
nitrifiers or in microsites
23
Sulfur oxidizing bacteria (not in chapter
5) Another important chemoautotroph is the Genus
Thiobacillus most important of chemoautotrophic
mineral oxidizers (elemental sulfur and sulfide
minerals). For elemental S 2S 3O2 2H2O
-------gt 4H 2SO42- Thiobacillus
thiooxidans
24
One important reaction carried out by these
bacteria is the oxidation of pyrite, FeS2, which
occurs commonly in mine spoils by Thiobacillus
thiooxidans and Thiobaccillus ferroxidans 4FeS2
1502 2H2O ? 2Fe2(SO4)3 4H 2SO42-
25
  • Some Important Heterotrophs
  • 1. Decomposers
  • 2. Nitrogen-fixing bacteria
  • Decomposing bacteria
  • Both aerobes and anaerobes
  • Very important for nutrient cycling convert
    nutrients from solid phase to ions which go into
    soil solution

26
  • Nitrogen fixers
  • Convert N2 gas in the atmosphere to ammonium
    (NH4) in the nodules of roots in certain plants
  • Very important source of N for soils and
    vegetation, especially in unpolluted areas
    soils have no mineral N source!
  • The atmosphere is 78 N2 gas but plants cannot
    utilize it because of the strong triple bond.
  • Nitrogen fixers take energy from host plants and
    convert this N to usable form using nitrogenase
    enzyme.

27
  • Two subdivisions of nitrogen fixers
  • Non-symbiotic N2 fixers Exist as free bacteria,
    but get energy from nearby organisms (plant
    rhizosphere, lichens)
  • Symbiotic N2 fixers live in plant roots, get
    energy from plant carbohydrates (heterotrophic)

28
  • Symbiotic N fixers include both bacteria and
    actinomycetes
  • Rhizobium bacteria
  • Associated with the root nodules of legumes
  • (e.g., Lupine, clover, alfalfa, soybean).
  • Can fix up to 300 kg ha-1 yr-1 (atmospheric
    deposition 1-25).

29
  • Frankia spp. actinomycetes
  • Various tree and shrub species (Alnus, Myrica,
    Elaeagnus, Ceanothus, Cuasarina)
  • These are more important than legumes in
    forests. Can also fix up to 300 kg ha-1 yr-1
    (atmospheric dep 1-25).

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31
Symbiotic N fixers Frankia actinomycetes Excessiv
e N fixation has been shown to cause
nitrification, nitric acid formation, nitrate
leaching, and soil acidification in red alder
32
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34
  • Free living N-fixers
  • Do not need a host plant
  • Usually fix much less than symbiotic fixers
  • Aerobes Azotobacter, A. beijerinckia, (hetero)
  • Anaerobes Clostridium, (most common)
  • Blue-gree algae (Cyanobacteria).
  • Often associated with plant roots present in
    cryptogamic/biotic crusts.
  • Believed to be first fixers 2-3 billion years
    ago.

35
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36
  • Actinomycetes
  • 5-20 µm dia, 0.1 - 1 m long (filaments, but more
    similar to bacteria)
  • Morphologically transitional from bacteria to
    filamentous fungi
  • Unicellular, slender branced mycelium
  • Numerically second only to bacteria
  • Aerobic, like pH gt 5
  • Active in decay of cellulose and other organics
    (hetero)
  • Frankia genus active in nitrogen fixation (as
    noted above)
  • Some produce antibiotics (exudates which kill
    bacteria)

37
57 Soil Viruses and Viroids
  • Non-cellular
  • Non-living nucleic acids with a coating
  • Cause many plant diseases often spread by
    carriers control is to control the carriers
  • Prion nucleic acids with no coat
  • Viroid no coat around RNA
  • Virus coat
  • Soil can function as a repository chronic
    wasting (mad cow disease).

38
58 Conditions for Microbial Activity
  • Moisture near FMC
  • pH near 7 for bacteria do not do well below pH
    5
  • Temp biological activity increases 2x as temp
    goes from 10 to 20 C
  • Exceptions
  • Psychrophiles can grow at lt5 C, opt at 15 C
  • Mesophiles slight growth at 0 C, little growth
    gt40 C, opt at 25-37 C
  • Thermophiles tolerate 45-75 C, opt at 55-65
    (composters)

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40
  • Encouraging good microbes
  • Inoculation
  • Lime
  • Minimize sterilization
  • Maintain SOM
  • Avoid contamination
  • Avoid stress (drought, temp, etc)

41
  • Controlling bad microbes
  • Start with clean plants
  • Sanitation
  • Minimize mechanical damage
  • Control water Not too humid
  • Control soil acidity
  • Control infestations quickly (spray)

42
59 Composition of Organic Matter (Soil Organic
Matter SOM)
  • 40-50 C, then H, O, N, P,.
  • C-chains
  • Humic substances colloidal, amorphous,
    polymeric, dark-colored materials end products
    of extensive decomposition
  • Functional breakdowns of humus
  • Humic acid soluble in NaOH, but not in HCl
  • Fulvic acid soluble in both
  • Humin insoluble in both
  • SOM is very complex, from simple sugars to
    complex humic substances.

43
510 Decomposition of SOM Activation energy
what it takes to push the reaction over the edge
(fire is example)
Energy needed to sustain the reaction
Energy
Reaction
44
Enzymes lower activiation energy by acting as
catalysts (substances which activate the
reaction but are consumed by it) Insight on p.
145, Table 5-4 are examples of enzymes Products
of decomposition nutrients are converted from
the organic form (not useable by plants) to
inorganic forms (available to plants and
microbes) CO2, NH4, H2PO4-, SO42-, Ca2, K,
Mg2, Na, H2O
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46
Factors affecting decomposition
  • Moisture too dry (aridisols) or too moist
    (histosols)
  • Temperature
  • Nitrogen Carbon to nitrogen ratio (CN ratio)
    a fundamental property of soils that relates to
    nitrogen status

47
Both litterfall and decomposition increase with
mean annual temperature however, decomposition
increases more rapidly and thus O horizon mass
decreases
Decomposition
O Horizon mass
Litterfall
Mean Annual Temp
Mean Annual Temp
48
Cold ecosystem Warm Ecosystem
CO2
Litterfall
CO2
Litterfall
O Horizon mass
49
  • Other factors affecting the accumulation of soil
    organic matter
  • Texture very important for SOM accumulation
    surfaces adsorb (especially allophane and
    sesquioxides)
  • pH too low inhibits decomp
  • Disturbance ploughing is the best example (lost
    40 SOM in Great Plains since agriculture) - this
    allowed early settlers to grow crops w/o
    fertilizer (that is over now) and create dust
    bowls.

50
511 Effects of Soil Organic Matter
  • Improve physical and chemical properties
  • Aeration, WHC, structure, drainage
  • Ion exchange, chelation
  • Source of available nutrients
  • Allelopathy

51
  • CN Ratio of Organic Organic Matter
  • In order for soil microbes to decompose most
    litter types, they must initially incorporate N
    from the soil.
  • Thus, inputs of high CN ratio litter can cause
    N deficiency to plants unless accompanied by
    fertilization.
  • As C is lost at CO2 gas, the C/N ratio of the
    litter decreases to a value ranging of about 201
    N is released from decomposing litter
  • (Figure 5-9)

52
CN Ratio of Organic Organic Matter Compare the
CN ratio of decomposers (microbes) with that of
the litter they must decompose
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54
  • Nitrogen Cycling in Soil
  • CN ratios of litter substrate is often much
    greater than in microbe bodies
  • Therefore, microbes keep the N, release the C as
    CO2, thereby reducing the CN ratio

Carbon
CO2
Nitrogen
Microbes CN 12
Organic Substrate CN 12 to 200
55
  • Nitrogen Cycling in Soil
  • In order to consume very high CN ratio material
    (such as wood), microbes may need to import
    ammonium (NH4) from the soil
  • This is called N immobilization
  • It steals available N from plants!

Plants
Carbon
CO2
X
Nutrients
Immobilization
Microbes CN 12
Organic Substrate CN 200
NH4
56
  • Nitrogen Cycling in Soil
  • Once microbes have satisfied their N demands,
    they release N as ammonium (NH4) during
    decomposition as they continue to get energy from
    the organic C
  • This is called N mineralization, and it provides
    available N to plants

Plants
Carbon
CO2
Nutrients
Mineralization
Microbes CN 12
Organic Substrate CN 12 to 200
NH4
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58
CN Ratio of Organic Organic Matter
As a rule of thumb At CN gt201, NH4 is
immobilized At CN lt 201, NH4 is mineralized
CN lt 201
Organic matter plus microbe N
NH4
CN gt201
59
512 Organic wastes
  • Animal manure
  • Municipal sludge application to land instead
    of dumping in water
  • Composting
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