5. Soil Texture
SIZE AND DISTRIBUTION OF PARTICLES
Silt Loam- has a broken appearance, appears
cloddy, lumps can be broken readily; when
pulverized, it feels soft and floury.
Clay Loam- breaks into clods or lumps that are
hard when dry, does not crumble readily but
works into a heavy compact mass.
Clay- fine-textured soil that usually forms very
hard lumps or clods when dry, usually sticky
when wet, individual grains can be seen or felt
readily.
6. Soil Texture
Sand -loose and single-grained, individual grains
can be seen or felt readily, when moist, it
forms a cast but crumbles when touched.
Sandy Loam-high percentage of sand but having
enough silt and clay to make it somewhat
coherent, If squeezed when moist, a cast can
be formed without breaking readily
Loam.- A loam is soil having a relatively even
mixture of different grades of sand, silt, and
clay. Squeezed when dry, it forms a cast which
can be handled freely without breaking.
7. EFFECT OF SOIL TEXTURE
ON
ROOT PENETRATION
FIGURE: Development of
root system of a yellow
birch seedling in sand an
loam soil. Both soils had
adequate supplies of water
and oxygen. (Redmond,
1954)
11. influences the rate at which
water and air enter and move
through the soil
affects root penetration and
the nutrient supply of the soil
Soil Structure
13. Soil Porosity
Soil porosity is affected mostly by
soil aggregation, texture, root
activity, entrapped gases, and by
burrowing insects, worms, and other
animals.
The structure as well as the porosity
of the soil is extremely vital for the
reduction of the risk of soil erosion
and increase the water infiltration.
14. Soil Porosity
Clay- poor soil aeration when wet
Sands- good aeration or gaseous
diffusion
50% porosity is desirable, good
balance between the retention of
water for plant use and an oxygen
supply for root respiration.
15. Consistence is the resistance of
the soil to deformation or
rupture.
determined by the cohesive and
adhesive properties of the
entire soil mass.
Soil Consistence
16. deals with the strength and nature
of the forces between the sand,
silt, and clay particles
important for tillage and traffic
considerations.
Clay soils can become sticky when
wet, and thus make hoeing or
plowing difficult.
Soil Consistence
17. Tilth
physical condition of the soil that
refers to the ease of tillage.
depends on the degree and
stability of soil aggregates.
refers as fitness of soil as a
seedbed,
desirability for seedling emergence
and root penetration.
18. SOIL Erosion
Reasons:
• Insufficient
vegetative cover
• Growing crops on
non-suitable soils
for cultivation
• Improper tillage
How to reduce:
• Using soil to produce
crop w/c it is
suitable
• Using adequate
fertilizer and lime
• Use proven soil
preparation and
tillage methods
19. SOIL COMPACTION
The changes in soil porosity, owing
to compaction are caused by the
long-term effects of cropping and
tillage and by the pressure of
tractor tires, animal hooves, and
shoes
20. Results of SOIL COMPACTION
decrease in total pore space
decrease in macropore space
increase in micropore space.
23. Bacteria
Single celled
A gram of fertile soil commonly
contains 10' to 10 10 bacteria.
Most are heterotrophs
Most are aerobes and require a
supply of oxygen
Some are anaerobic
24. Fungi
heterotrophs that vary greatly in size
and structure.
Mold mycelia are commonly seen
growing on bread, clothing, or leather
goods.
Rhizopus is a common mold that grows
on bread and in soil.
Their tolerance for acidity makes them
particularly important in acidic forest
soils.
25. Nematodes
Roundworms
most abundant animals in soils.
round shaped
free-living and inhabit the water films
that surround soil particles.
can be grouped into those that feed
on: (1) dead and decaying organic
matter, (2) living roots, and (3) other
living organisms as predators.
26. Arthropods
have an exoskeleton and jointed legs
have heart and blood system, and
usually
a developed nervous system.
most abundant are mites and
springtails.
include spiders, insects millipedes,
centipedes, wood lice, snails, and
slugs.
27. The Role of Organisms in
Soil Health
Aids in the decomposition of organic
matter (bacteria & fungi)
Releases compounds which are accumulated in
the deeper layer of soil as minerals and are
carried by underground water as nutrients
absorbed by plants
Assists nutrient cycle and release of
energy as heat
28. The Role of Organisms in
Soil Health
Breaking of aggreggates
Aids in the penetration of water
Aids in the development of porosity
Burrowing animals entraps gases for aeration
30. ♣ exchange of nutrient elements
between the living and non
living parts of the ecosystem.
♣ conserves the nutrient supply
and results in repeated use of
the nutrients in an ecosystem.
NUTRIENT CYCLES
31. ♣ Mineralization
♣ Immobilization
NUTRIENT CYCLING
PROCESS
conversion of the elements in organic matter into
mineral or ionic forms such as NH3 , Cat-, H2P04 -
, S04 2- , and K+.
uptake of inorganic elements (nutrients) from the
soil by organisms and conversion of the elements
into microbial and plant tissues. These nutrients
are used for growth and are incorporated into
organic matter.
36. NITROGEN FIXATION
Biological
Industrial
Atmospheric
• fixed by lightning
and other ionizing
phenomena of the
upper atmosphere
• converted as HNO3
• added to soils in
precipitation
• Via Haber-Bosch
process
• Via nitrogen fixing
bacteria (legumes)
symbiotic Non-symbiotic
• blue
green
algae
38. NITROGEN CYCLE
Nitrification is the biological oxidation of
ammonium (NH4') to nitrite (N02 ) and to
nitrate (N03- )
two-step process, with nitrite (NO 2-) as the
intermediate product.
40. PHOSPHORUS
Most phosphorus occurs in the mineral
apatite in igneous rocks and soil parent
materials.
Fluorapatite (𝐶𝑎10 𝑃𝑂4)6 𝐹2 is the most
common apatite mineral.
Phosphorus plays an indispensable
role as a universal fuel for all
biochemical activity in living cells.
Sedimentary nutrient cycle-> SLOW
43. PHOSPHORUS CYCLE
The potential for P fixation tends to
maintain phosphorus in insoluble forms
and, therefore, the phosphorus
concentration in the soil solution is very
low.
Thus, mass flow cannot supply plants with
sufficient phosphorus except in unusual
cases.
As a result, most of the H 2PO4 - at root
surfaces has been moved there by
diffusion.
45. POTASSIUM CYCLE
When plants are dormant and leaching is minimal,
weathering of potassium minerals results in an
increase in solution potassium, followed by an
increase of exchangeable potassium, followed by an
increase in the amount of fixed potassium.
Weathering and subsequent loss of potassium by
leaching with time can deplete the soil of potassium
minerals and create soils with few potassium
minerals and very low available potassium.
This is generally true for intensively weathered soils.
Potassium does not complex with organic compounds
46. Sulfur exists in some soil minerals, including
gypsum (CaSO4-2H20).
Mineral weathering releases the sulfur as
sulfate ion which is absorbed by roots and
microorganisms.
released as sulfur dioxide (SO2) into the
atmosphere by the burning of fossil fuels
accumulates in soils as organic sulfur in plant
residues and is then mineralized to S04 2 -.
Plants may absorb sulfur in the air through leaf
stomates.
SULFUR CYCLE
48. contributes to the development of soil acidity.
Sulfate is adsorbed onto the surfaces of iron
and aluminum oxides and onto the edges of
silicate clays, where aluminum is located.
Critical to formation and fumction of protein
Found in soil as SOM
SULFUR
49. MAGNESIUM
Magnesium is a constituent of chlorophyll.
magnesium deficiency results in a
characteristic discoloration of leaves.
Sometimes, a premature defoliation of the
plant results. The chlorosis of tobacco,
known as sand drown, is due to magnesium
deficiency.
Cotton plants suffering from a lack of
magnesium produce purplish-red-colored
leaves with green Veins.
55. Why Soils are acidic
Rainfall and leaching
Acidic parent material
Organic matter decay
Harvest of high yielding crops
56. 1) In all soils respiration by roots and
other soil organisms produces carbon
dioxide that reacts with water to form
carbonic acid (H2CO3). This is a weak
acid, which contributes H+ to the soil
solution
Sources of Soil Acidity
𝐶𝑂2 + 𝐻2 𝑂 → 𝐻2 𝐶𝑂3
57. 2) the mineralized nitrogen and sulfur
from the organic matter are oxidized
to nitric and sulfuric acid
3) natural or normal precipitation
reacts with carbon dioxide of the
atmosphere and the carbonic acid
formed gives natural precipitation a
pH of about 5.6.
Sources of Soil Acidity
59. CONCLUSION
Soils has bio-physico and chemical
properties
Soil physical structure ad texture
influences the rate at which water and
air enter and move through the soil
affects root penetration and the nutrient
supply of the soil
Soil organisms play a major role in
formation of soils and in nutrient cycling
60. CONCLUSION
Living organisms need many
nutrients to survive. Vast cycles
makes nutrients available for reuse
by transforming and circulating them
thru the atmosphere, hydrosphere,
lithosphere and biosphere
Soil pH is needed for managing
nutrient availability, effect on soil
Organisms, toxicities in acid soils,
preferences of plants
61. REFERENCES
Alberto, A.M.P., (2006). Basic Ecology. (2nd ed) Nueva Ecija: CLSU CERDS
Albers, C., Fenton M., & Ketterings Q. (2008) Cornell University Agronomy Fact Sheet
series: Retrieved August 29, 2016 from
nmsp.css.cornell.edu/publications/factsheets.asp.
Allaby, M. (2000). Basics of Environmental Science. (2nd Ed) London: Taylor & Francis e-
Library
Bharucha, E. (2004). Environmental Studies: Undergraduate Courses of all branches of
higher education (Dunster, C. & Patel B., Eds). University Grants Commission New Delhi
Chauhan A, Mittu B (2015) Soil Health - An Issue of Concern for Environment and
Agriculture. J Bioremed Biodeg 6: 286. doi:10.4172/2155-6199.1000286
Daniels, W. L. Basic Soil Science. Retrieved August 29, 2016 from
http://pubs.ext.vt.edu/430/430-350/430-350_pdf.pdf &
http://www.cses.vt.edu/revegetation/
Foth, H. D. (1990). Fundamentals of Soil Science. (8th Ed). United States of America:
John Wiley & Sons.
62. REFERENCES
Gaur, R. C. (2008). Basic Environmental Engineering. New Delhi, India: New Age International (P)
Ltd, Publishers
JOHNSON, G. V., W. R. RAUN, H.N ZHANG, and J. A. HATTEY. 2000.Oklhoma soil fertility
handbook, Department of Plant and Soil Sciences, Oklahoma State University, Stillwater, OK
74078
Lehman, R. M., et al. (2015). Soil Biology for Resilient, Healthy Soil. Journal of Soil and Water
Conservation 70 (1):12A-18A
Prasadini P., & Lakshmi G. S. Environmental Science BIRM 301 Study Material. Dept. of
Environmental Science & Technology, College of Agriculture, Rajendranagar
Soil Quality Kit-Guides for Educators. United States Department of Agriclture Natural resources
conservation service
Soil Taxonomy (2nd edition) Soil Survey Staff. 1999. USDA-NRCS, Washington, DC Agriculture
Handbook 436 Retrieved August 29, 2016 from
http://www.nrcs.usda.gov/wps/portal/nrcs/detail/national/nedc/training/soil/?cid=nrcs142p2_0
53577
Editor's Notes
Texture is a major determining factor for water holding capacity. Fine-textured soils (high percentage of silt and clay) hold more water than coarse-textured soils (sandy).
Structure modifies the influence of texture with regard to water and air relationships and the ease of root penetration.
Blocky- good air and water movement
Prismatic- poor air and water movement
Platy- air and water movement is restricted
Granular- characteristics of A horizons
Platy- common in E horizons
blocky- common in B horizons u also in A
Tillage promote soil compaction
among the smallest living organisms, and exceed all other soil organisms in kinds and numbers.
Heterotrophs- requires complex N and C for metabolic synthesis
typically grow or germinate from spores and form a threadlike structure, called the mycelium.
readily extend their tissue and penetrate into the surrounding environment
Actinomycetes refers to a group of bacteria with a superficial resemblance to fungi.
Also called round worm
Under a 10-power hand lens they appear as tiny transparent threadlike worms
They lose water readily through their skin, and when soils dry or other unfavorable conditions occur, they encyst, or form a resting stage
can reactivate when conditions become favorable.
The services provided by soil biota include biogeochemical regulation, nutrient retention and delivery; symbiotic and compensatory associations; biodegradation/ bioremediation of wastes, pollutants and agrochemicals; pathogen dynamics; soil structure and stability; and weed dynamics. These lead to contribution to chemical and physical processes in the soil such as carbon, nitrogen and phosphorus cycles; decomposition; nitrogen fixation; microbial degradation; host-pathogen interaction; soil aggregation and porosity; building of organic matter; and germination & growth
Evaporation-takes place mostly in ocean
Transpiration- water stored in plant tissue diffuses thru plant membrane and enters the atmosphere as water vapor
Precipitation- may be simultaneous evaporation, may infiltrate the soil and absorbed by plants
may run-off to joint streams and rivers
May sink in ocean
Carbon- Main constituent of living organisms
Serves as backbone components of carbohydrates, proteins and lipid
Carbon is cycled primarily thru photosynthesis and respiration
Plants obtain CO2 from atmosphere and use it to produce glucose and O2
Plants, animals and decomposers return CO2 to atmosphere thru respiration
Some CO2 is returned into atmosphere via burning of organic matter
CO2 trapped in rock or fossil fuels can be cycled via erosion, volcanic eruptions or fossil fuel combustion
The reservoir of nitrogen for plant use is essentially that in the atmosphere, N2 . N is an integral component of amino acids w/c are the building blocks of proteins
Bacteria (rhizobium sp) infect the root of legume and cause nodule to form converts free N to NH3
Most nitrogen fixation is biological, being either symbiotic or nonsymbiotic. Nitrogen-fixing organisms contain an enzyme, nitrogenase, which combines with a dinitrogen molecule (N 2 ) and fixation occurs in a series of steps that reduces N2 to NH3. Molybdenum is a part of nitrogenase and is essential for biological nitrogen fixation. The nitrogen-fixing organisms also require cobalt
Nitrogen is used to build protein tissues. N compounds are returned to soil when plants and animals die or when animals give off waste (urea)
Bacteria and fungi break down dead organisms reducing to amino acids
Some NO3 are carried into oceans, some become part of sediments and lost in cycle
Denitrifying bacteria reduces NO3 to N2 and released back in atmosphere
High-energy adenosine triphosphate (ATP) bonds release energy for work, when converted to adenosine diphosphate (ADP).
Phosphorus is also an important element in bones and teeth.
Phosphates are weathered and transported by wind and water whre they exist as dissolved phosphates
Absorbed by plants for use in making of their tissues
Plants are eaten by animals and when they die, phosphatizing bacteria break down these products and return phosphates to soil
Much are leached or washed away in ocean
The phosphate ion other ions in the soil solution resulting in precipitation and adsorption to mineral colloids that convert the phosphorus to an unavailable or fixed form become encapsulated (occluded) by iron and aluminum oxides. As a result, before plant can reabsorbed them, they are deposited in sediment
As soils become acid, phosphorus is fixed as iron and aluminum phosphate. In acid soils, phosphorus released by dissolution of apatite is gradually converted into iron and aluminum phosphates. Eventually, in intensively weathered soils rich in iron and aluminum oxides, the crystalline forms of iron and aluminum phosphate
The K+ appears in the soil solution or is adsorbed onto a cation exchange site. An equilibrium tends to be established between the solution potassium and exchangeable potassium. As weathering proceeds, in the absence of the removal of K+ from the soil by plant uptake or leaching, there is a buildup of exchangeable potassium as a result of weathering. The exchangeable potassium maintains a quasi-equilibrium with the potassium entrapped or fixed, as shown in. Fixation is the reverse of the weathering of mica and occurs as the amount of exchangeable potassium increases and K+ move back into voids where interlayer potassium weathered out at an earlier time. Release, the opposite of fixation and is encouraged when plant uptake and leaching , result in reduced solution potassium. A reduced concentration of solution potassium is followed by reduced exchangeable potassium, which is then followed by the release of fixed potassium.
Potassium enhances the synthesis and translocation of carbohydrates, thereby encouraging cell wall thickness and stalk strength. A deficiency is
sometimes expressed by stalk breakage, or lodging.
Normally, this occurs in fall and winter in minimally and moderately weathered soils. When plant uptake and leaching occur, normally in spring and summer, there is a decrease in solution potassium, followed by a decrease of exchangeable potassium, and then a decrease in the amount of fixed potassium.
Plants that have the greatest need for sulfur include: cabbage, turnips, cauliflower, onions, radishes, and asparagus. Intermediate sulfur users are legumes, such as alfalfa and cotton and tobacco. Sulfur deficiency symptoms are similar to nitrogen in that sulfur-deficient plants are stunted and light-green to yellow in color.
Plants that have the greatest need for sulfur include: cabbage, turnips, cauliflower, onions, radishes, and asparagus. Intermediate sulfur users are legumes, such as alfalfa and cotton and tobacco. Sulfur deficiency symptoms are similar to nitrogen in that sulfur-deficient plants are stunted and light-green to yellow in color.
Calcium functions in the plat cell wall development and formation. Ca2+ is held tightly on negatively charged clay and organic particles and abundant in arid and semi-arid areas,
Sources are lime (CaCO3), gypsum (CaSO4)
The pH requirement of some disease organisms is used as a management practice to control disease. One of the best known examples is that of the maintenance of acid soil to control potato scab. Earthworms are inhibited by high soil acidity. Peter Farb (1959) relates an interesting case in which soil pH influenced both earthworm and mole populations.
The common range of soil pH under natural conditions is 5.0-9.0. for each pH change of 1 unit, the concentration of H+ changes 10x. So much more acidic is a pH 4.0 soil when compared with pH 7.0 soil?
Normal range is 3.8-8.5. acidic soils are usually due to S oxidation, when soils are alkaline, sodium dominates
In a calcareous soil, OH - from carbonate hydrolysis reacts with any H + that is produced to form water; thus, calcareous soils remain alkaline in spite of the near constant production or addition of H+. Development of neutrality, and eventually acidity, is dependent on the removal of the carbonates.