Objectives:
1. Understand the terrestrial environmental from an integrated physical,
chemical and biological perspective.
2. Define a surface soil, the vadose zone, and the saturated zone.
3. Define components of soil discussed in class such as texture, pore size
distribution, organic matter, soil structure, interaggregate and
intraaggregate pores, cation exchange, soil water potential.
4. Understand how soil water potential relates to microbial activity.
5. Understand the basics of contaminant sorption and microbial sorption.
6. Understand how microbial activity can influence the soil atmosphere.
7. Be able to describe the types, numbers, and relative activities of
microbes found in surface soil, vadose zone, and saturated zone
environments.
8. Discuss the respective competitiveness of the bacteria,
actinomycetes, and fungi in soil.
Chapter 4 - The Terrestrial Environment
Spontaneouswater
movement
Saturated zone
Capillary fringe (nearly saturated)
Vadose zone (unsaturated)
Surface soil (unsaturated)
Sca
le c
an r
ang
e fr
om
10
to 1
00’s
of m
ete
rsWater table
X
Surface soils
Vadose zone
Saturated zoneshallow aquifers
intermediate aquifersdeep aquifers
1) 45% mineral (Si, Fe, Al, Ca, K, Mg, Na) The two most abundant elements in the earth’s crust are Si (47%) and O (27%)
Quartz = SiO2
Clay minerals are aluminum silicates
Nonsilicates = NaCl, CaSO4 (gypsum), CaCO3 (calcite)
Pore spaceMineral
OM
Components of a typical soil
2) 50% pore space
3) 1 to 5% organic matter
Soil texture – this defines the mineral particle sizes that makeup a particular soil.
particle diameter Surface to volume ratio range (mm) (cm2/g) Sand: 0.05 – 2 mm 50
Silt: 0.002 – 0.05 mm 450Clay: 0.0002 – 0.002 mm 10,000
Pore size distribution is important when one considers movement of fluids and of microbes through a porous medium. Protozoa and bacteria will have difficulty moving through even sandy porous media.
Similarly fluids like water move more easily through large pores, not because the water molecules are too large, but because there is less resistance to water movement through larger spaces.
Fine Coarse
Num
ber
of
pore
s
Fine CoarseN
umb
er o
f po
res
Fine Coarse
Num
ber
of
pore
s
C lay texture Loam texture Sand texture
The amount of clay and organic matter in a soil influence the reactivity of that soil because they both add surface area and charge. Because large amounts of clay make the texture of the soil much finer, the average pore size is smaller.
Texture and pore size distribution
Filtration is important when the size of the bacterium is greater than 5% of the mean diameter of the soil particles
20 um 0.6-20 um 0.02–0.6 um
Pore size
5% of the mean pore diameter
The major input of organic matter in soil is from plant, animal, and microbial biomass. Humus is the ultimate product of degradation of organic matter. Humus is aromatic in character. This is because the humus backbone is derived from the heterogeneous plant polymer lignin which is less readily degradable than other plant polymers (cellulose and hemicellulose).
Core molecules for organic humus
Organic Matter
Humus has a three dimensional sponge-like structure that can absorb water and solutes in the water. Humus is only slowly utilized by soil organisms and has a turnover rate of 1 to 2% per year. In general soils with higher organic matter contents have higher numbers of microbes and higher levels of activity.
Humus shares two properties with clay: it is highly charged and it has a large surface area to volume ratio.
The quantity of organic matter found in soil depends on climate. Soils found in temperate climates with high rainfall have increased levels of organic matter. Levels of organic matter found in soil range from essential no organic matter (Yuma, AZ) to 0.1% organic matter (Tucson, AZ) to 3 to 5% organic matter (midwest) to 20% organic matter (bogs and wetlands).
Why do peat bogs have very low microbial activity? (see Info Box 4.2)
Bogs and wetlands
Organic matter > 20%Bogs cover 5 – 8% of the terrestrial surface
Humic-like substances secretionhydrophobic region
Polysaccharide secretion - hydrophobic regionbinding of clay particles
Fungi
Physical entanglement
Soil aggregate
Polysaccharide secretionbinding of clay particles
Bacterial colonies
Cross-section
Surface Soils
10 structure = soil particles + organic matter (humus) + roots +
microorganisms20 structure = aggregate or ped = stability
C
1 micron
Fissure
Micro-environment =oriented, packedand glued clay
Non perturbed clay
Polysaccharide secretion
Cell wall
Fungal hyphae
Clay Particles
Soil aggregates are formed and stabilized by clay-organic complexes, microbial polysaccharides, fungal hyphae and plant roots.
See Info Box 4.4 for a special case of aggregation, cryptobiotic crusts.
Interaggregate pore space ( m to mm in size)
Aggregate particle
Intraaggregate pore space(nm to m in size)
Enlargement
Soil aggregates are associated with relatively large inter-aggregate pore spaces that range from um to mm in diameter. Each aggregate also has intra-aggregate pore spaces that are very small, ranging from nm to um in diameter.
Intra-aggregate pores can exclude bacteria (called micropore exclusion). However, after a spill, contaminants can slowly diffuse into these pores. This creates a long-term sink of pollution as the contaminants will slowly diffuse out again.
2 mm
Assume a soil aggregate that is 2 x 2 x 2 mm. Further assume that the volume of the aggregate is 50% pore space. How many pores of diameter 15 um does the aggregate have? How many pores of 50 um?
(the volume of a sphere is: 4/3π r3)
Just how many pores are there?
2 mm
Calculation for 15 um pores:
The volume of the aggregate is 2 mm x 2 mm x 2 mm = 8 mm3
Pore space is 50% of 8 mm3 = 4 mm3
A pore of 15 um diameter has volume = 4/3 π (7.5 um)3 = 1.77 x 103 um3
4 mm3 (1000 um)3 / 1.77 x 103 um3 = 2.3 x 10 6 pores of 15 um per aggregate! mm3 pore
2 mm
In soil 80 to 90% of the bacteria are attached to surfaces and only 10-20% are planktonic. Cells have a patchy distribution over the solid surfaces, growing in microcolonies. Colony growth allows sharing of nutrients and helps protect against dessication and predation or grazing by protozoa.
Where are the bacteria?
Interaction of contaminants and microbes with soil surfaces
Soils have an overall net negative charge that comes from clay oxides, oxyhydroxides, and hydroxides. The negative charge attracts positively charged solutes from the soil solution in a process called cation exchange. Organic matter also provides a net negative charge and adds to the cation exchange capacity of a soil.
Normally, soil cations such as Na+, K+, or Mg2+ bind to cation exchange sites. However, when a positively charged metal contaminant such as lead (Pb2+) or an organic contaminant are present they can displace these cations. This leads to sorption of the contaminant by the soil.
Cation Exchange-
-- -
-
-- -
-
--
-
--
-
-- - -
-
--
-
--- - -
---
---
--
-
-
-- -
-
--
+
+
+
+
+
+
++
++
+
+ +
+ +
++
++
+
+
++
++
+
+
++
++
++
+
+
+ + +
++
+
+
+
++
+
+
+
+
K +Mg2+
Al3+
Pb 2+
+ +
+
++
+
+
+
+
+
+
+
+
+
+
++
+
+
+
+
+
+
+
+
+ +
+++
+
(Metal contam inant)
Na+
Na +
Clay particle+
+
++
++
+
Add
+
-++-++
-++
-++ -++-++-++
-++ -++
-
-- -
-
-- -
-
--
-
--
-
-- - -
-
--
-
--- - -
---
---
--
-
-
-- -
-
--
+
+
+
+
+
+
++
++
+
+ +
+ +
++
++
+
+
++
++
+
+
++
++
++
+
+
+ + +
++
+
+
+
++
+
+
+
+
K +Mg2+
Al3+
Pb 2+
+ +
+
++
+
+
+
+
+
+
+
+
+
+
++
+
+
+
+
+
+
+
+
+ +
+++
+
(Metal contam inant)
Na+
Na +
Clay particle+
+
++
++
+
Add
+
-++-++
-++
-++ -++-++-++
-++ -++
Similarly, bacteria are sorbed to soil. In this case the bacterium, which like the soil has a net negative charge, is sorbed through a cation bridge.
--
--
--
-
Clay particlenegatively charged
-
Bacterium negativelycharged
Mg2+
Divalent cation
++
+
+
+
+
+
+ ---
Attachment of bacteriumthrough cation bridging
+
Nonpolarorganic molecules
Organic matter
Clay
A second mechanism for sorption of contaminants is hydrophobic binding. Hydrophobic sites on the soil surface are created when organic matter is present. Polar groups in the sponge-like organic matter structure face the outside while non-polar groups are in the interior of the sponge. Nonpolar molecules are attracted to the nonpolar sites in the organic matter resulting in hydrophobic binding.
--
--
--
-
-+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ ++ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+
+
+
+
+
+
+ +
+
+
+
+
+
+
+
+
+
+
+
+
+
+
+
+
+
++
+
+
+
+
+
+
+
+
+
+
+++
+
+
+
+
+
+
+
+
+
+
+
+
+
+
+
++
+
+
+
++
+
+
+
+
+
+
+
+
+
+
+
+
+
+-
--+
+
+
Fertilizers, pesticides spilled fuel, and irrigation runoff
Plant roots
Cation exchange
Precipitation from solutionand parent minerals
--
-
-
---
--- -
--
--
--
-
PPPPPPPPPP
PPPP
P PPPPPP PP PP P PPPPPPPPP
PPPPPPPPP
PPP P
PPPPP PPPP PP PPPPPPPPPPP
PPPPPPPPP
PPP P
PP PPPPP PPP PPP PPPPPPPPP
PPPPPPPPPP
P PP PPPP PPPP PPP PP
PPPPPPPPP
PPPPPPPPP
PPPP
PPPPP PPPP PP P PPPPPPPPPP
PPPPPPPPPP
PPPP
PPPPPPP PP PP P PPPPPPPPP
Microorganisms
+ +
+ ++ +
+ + +
+
+
+
+ + +
+ +
+ +
+ +
+ +
+ +
+ +
+
+
+++
+
+
+
+++
+
+++
+++
+
+
+
+
+
+
+
+++
+
+++
+
+
-
-
-
-
-
-
-
-
-
+
+
+
+
+
+
+
+
+
+
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+ +
+++
+
++
+
++
+
+
+
+
+
+
+++
+
+
+
+
+
+ +
Soil Solution
The soil solution is a constantly changing matrix composed of both organic and inorganic solutes in aqueous solution.
Water movement and soil water potential
Soil water potential depends on how tightly water is held to a soil surface. This in turn depends on how much water is present.
Surface forces have water potentials ranging from –10,000 to –31 atm.
Capillary forces have water potentials ranging from –31 to –0.1 atm. Optimal microbial activity occurs at approximately -0.1 atm.
At greater distances there is little force holding water to the surface. This is considered free water and moves downward due to the force of gravity.
Soil air
FREE WATER
Gravitationalforces
Ca
pilla
ry f
orce
s
Su
rfa
ce fo
rces
Soi
l pa
rtic
les
% Saturation ofthe soil pore
100%0%
A m
Soil air
Increasing distance from particle surface
Soil air
FREE WATER
Gravitationalforces
Ca
pilla
ry f
orce
s
Su
rfa
ce fo
rces
Soi
l pa
rtic
les
% Saturation ofthe soil pore
100%0%
A m
Soil air
Increasing distance from particle surface
Soil air
FREE WATER
Gravitationalforces
Ca
pilla
ry f
orce
s
Su
rfa
ce fo
rces
Soi
l pa
rtic
les
% Saturation ofthe soil pore
100%0%
A m
Soil air
Increasing distance from particle surface
Soil air
FREE WATER
Gravitationalforces
Ca
pilla
ry f
orce
s
Su
rfa
ce fo
rces
Soi
l pa
rtic
les
% Saturation ofthe soil pore
100%0%
A m
Soil air
Increasing distance from particle surface
Soil atmosphere
The composition of the earth’s atmosphere is approximately 79% nitrogen, 21% oxygen, and 0.03% carbon dioxide. Microbial activity in the soil can change the local concentration of these gases especially in saturated areas.
0.03
0.3 – 3
Up to 10
20.9
18 - 20.5
0 - 10
78.1
78.1
>79
Atmosphere
Well-aerated surface soil
Fine clay/saturated soil
Carbon Dioxide (CO2)Oxygen (O2)Nitrogen (N2)Location
Composition (% volume basis)
Microorganisms in soil – an overview
• minor role as primary producers
• major role in cycling of nutrients
• role in soil formation
• role in pollution abatement
Bacteria
Culturable counts 106 – 108 CFU/g soil
Direct counts 107 – 1010 cells/g soil
Estimated to be up to 10,000 species of bacteria/g soil
Actinomycetes
Culturable counts 106 – 107 CFU/g soil
Gram Positive with high G+C content
Produce geosmin (earthy smell) and antibiotics
Fungi
Culturable counts 105 – 106/g soil
Obligate aerobes
Produce extensive mycelia (filaments) that can cover large areas.
Mycorrhizae are associated with plant roots.
White rot fungus, Phanerochaete chrysosporium is known for its ability to
degrade contaminants.
Highest numbers
Highest biomass
Numbers and types of microbes in typical surface soils
Comparison of bacteria, actinomycetes, and fungi
Bacteria Actinomycetes Fungi
Numbers highest intermediate lowest
Biomass --- similar biomass --- largest
Cell wall --- PEP, teichoic acid, LPS --- chitin/cellulose
Competitiveness most least intermediatefor simple organics
Fix N2 Yes Yes No
Aerobic/Anaerobic both mostly aerobic aerobic
Moisture stress least tolerant intermediate most tolerant
Optimum pH 6-8 6-8 6-7
Competitive pH 6-8 >8 <5Competitiveness all soils dominate dry, dominate high pH soils low pH soils
Example 1: A shallow coreKonopka and Turco (1991) compared microbial numbers and activity in a 25 m core that included surface soil, vadose zone, and shallow saturated zone samples.
Bacterial numbers and activity in surface soil, the vadose zone, and the saturated zone
Site was a 40 year old corn field at Purdue University
Surface soil
? ?
Shallow saturated zone
?
Vadose zone
Culturable counts (10-3 CFU/g)
AODC (10-7 cells/g)
Phospholipid (ug/g)
Compare the microbial numbers in the surface, vadose zone, and saturated regions.
Compare the microbial activity in the three regions in terms of:
1) lag time2) growth rate3) cell yield.
14C
O2
evo
lved
as
a %
of
the
carb
on
ad
ded
Days
80
60
40
20
0
Vadose zone sample
0 8 16 24 32
0 8 16 24 32
Surface soil sample80
60
40
20
0
Saturated zone sample
0 8 16 24 32
80
60
40
20
0
glucosephenol
Example 2: The deep vadose zone
A 70 m core was taken in the Snake River Plain in Idaho (Colwell, 1989).
Sample site
Direct counts (counts/g)
Culturable counts (CFU/g)a
Surface (10 cm) 2.6 × 106 3.5 × 105
Subsurface basalt-sediment interface (70.1 m)
4.8 × 105 50
Subsurface sediment layer (70.4 m)
1.4 × 105 21
TABLE 4.11 A comparison of microbial counts in surface and 70-m unsaturated subsurface environments
aCFU, colony-forming units.
Compare the direct and culturable counts between the surface samples and the deep vadose zone samples.
In 1987, a 470 m core was taken in the southeast coastal plain in South Carolina (Fredrickson et al., 1991). Culturable counts ranged from 103 to 106 CFU/g in a permeable sandy sample retrieved from between 350 and 413 m. Culturable counts were lower (non-detect to 104 CFU/g) in a low permeability sample taken between 450 and 470 m.
Example 3: The deep saturated zone
Compare the microbial counts measured in surface, vadose zone, and saturated zone samples presented in the 3 examples. What do these counts imply for activity in each of these regions?What do these counts imply for diversity in each of these regions?
More recently, (2001-2006), a series of water samples were taken from the saturated zone at depths of 0.72 - 3 km in the Witwatersrand Basin in central South Africa ( Gihring et al ., 2006 ). Total microbial numbers in the samples were estimated to be as low as 103 cells/ml. Diversity was low as shown by analysis of the 16S rRNA gene, which generated only an average of 11 bacterial OTUs from all the samples. Compare this to surface soils that have up to 6300 OTUs!
Summary and Reality CheckDespite the fact that there are microbes present in most subsurface samples, often in high numbers, the level of microbial activity in the deep subsurface is very very low when compared to activity in surface soils or in lake sediments.
101
10 -3
10 -5
10 -9
10 -13
Ra
tes
of C
O
pro
duc
tion
(mo
les/
liter
/ye
ar)
2
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