soil and water analysis: theoretical background and practical … course... · 2016. 6. 20. ·...
TRANSCRIPT
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Soil and water Analysis:
Theoretical background and practical
application
Dr. Adel Aly
Laboratory of Agricultural and Environmental Chemistry
IAM-Bari
ACLIMAS Training course on “AGRONOMIC AND ENGINEERING ASPECTS OF
ADAPTATION TO CLIMATE CHANGE IN MEDITERRANEAN AGRICULTURE”
Agricultural extension and service Center of the Litani River Authority - Kherbet Kanafar,
Bekaa, Lebanon 2-6 November, 2015
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SAMPLING - I
• The sampling consists in taking a small mass
(sample) from a great mass
• The sample must be representative of the whole
mass
• The concept of representativeness is the guidance
for all sampling procedures
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SAMPLING - II
• A representative sample is one that is considered
to be typical of the universe of concern and
whose composition can be used to characterize
the universe with respect to the parameter
measured (Taylor, 1988)
“The analysis cannot be better than the sample”
- an axiom
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SOIL SAMPLING - I
• The purpose of soil sampling is to obtain information
about a particular soil
• Any soil is characterized by several types of variation
and is not a homogeneous mass but a rather
heterogeneous body of materials (called “population”)
• In view of the variability of the soils, it seems
impossible to devise an entirely satisfactory method
for sampling
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SOIL SAMPLING – II
For any soil there are certain characteristics which
describe it. The true value of such characteristics
in the soil is called a parameter. The purpose of
sampling is to estimate these parameters with an
accuracy that will meet our needs at the lowest
possible cost.
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Principles of soil sampling
• Soil volumes, not areas, are sampled
• With the soils, variation and the heterogeneity
are the rule rather than the exception
• The details of sampling procedure should be
determined by the purpose for which the sample
is collected
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Principal sources of variability of
soil chemical and physical analysis
1. Sampling error
2. Sub-sampling error
3. Analytical error
The error due to sampling is generally greater than that due to sub-sampling and analytical procedures
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Main Types of soil sampling
• Systematic sampling
• Unsystematic (random) sampling
• Circle grid sampling
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Systematic sampling
• The systematic sampling plan is an attempt
to provide better coverage of the soil study
area than could be provided with the simple
random sampling plan.
• Systematic sampling collects samples in a
regular pattern (usually a grid or line transect)
over the areas under investigation.
• The samples are collected at regular intervals
in one or more directions
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systematic sampling I
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systematic sampling II
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Unsystematic (random) sampling
• The basis of most sampling plans in
environmental sampling is the concept of
random or probabilistic selection of the
sample to be collected and the subsample
that is to be analyzed.
• In random sampling of a site, each sample
point within the site must have an equal
probability of being selected.
• The same can be said for the selection of
particles within a sample
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“X” unsystematic sampling
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“W” unsystematic sampling
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circle grid sampling
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AUGER - I
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Sampling by shovel or spoon
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Laboratory sample collection
• Laboratory identification numbers are assigned
to the bulk soil samples
• In the laboratory database, a file corresponds to
each number; the file contain the most important
information about the soil sample
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Laboratory sample preparation
• Laboratory analyses of soil samples are generally
carried out on the air-dry, fine-earth fraction (< 2
mm)
• Generally the > 2 mm fraction is sieved, weighed,
and discarded; it is excluded from chemical and
physical analyses
• Stones and gravel Ø > 2 mm
• Fine earth Ø < 2 mm
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• sample homogenization
• aggregates crushing by pestle and mortar
• sieving to 2 mm
• If it is necessary, reduce the mass of sample
Sample preparation
X
Quartering method
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Fraction > 2 mm
1000sampledryweight
mm2fractiondryweight)kg/g(graveland
Stones
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Humidity (g/kg) = wet weight – dry weight (105 °C)
wet weight X 1000
Correction factor = wet weight (105 °C)
dry weight
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Sample preparation - I
• Reduction of the sample by the “quarter”
method
S
S
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Sample preparation - II
• Subdivision of the sample in two aliquots:
1. Moist sample for the analysis of pH, N, etc.
2. Dry sample (air drying) for the analysis of
further parameters
• Moisture content is determined on both aliquots
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Sample preparation- III
• Many analytical determination are performed on
very small portions of sample (< 1 g)
• In order to analyse a representative sample, it is
therefore necessary to further homogenize the
sample to very small particles ( < 0,5 mm)
• The mill could be performed through:
Ball mill
Blade mill
and by means of certified sieves
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manual mortar
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Certified sieve 28
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Automatic ball mill and blade mill
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Ball mill chambers
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Main parameters for evaluation of soil
fertility
• Particle-size analysis
• Electrical conductivity
• Organic Matter
• Exchangeable
potassium, calcium,
magnesium and
sodium
• pH
• Total carbonate
• Nitrogen
• Available phosphorus
• Cation exchange
capacity (CEC)
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Main chemical parameters for evaluation of
water quality for irrigation
• pH
• Electrical
conductivity
• Sodium
• SAR index
• Chloride (Cl-)
• Hardness
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pH
• Soil pH is probably the single most informative
measurement that can be made to determine soil
characteristics. It tells much more about a soil than
merely indicating whether it is acid or basic. For
example, availability of essential nutrients and
toxicity of other elements can be estimated
because of their known relationship with pH.
• It is the first measurement that is made in
laboratory
• On the basis of the pH value, the analyst
sometimes will choose the method of analysis (for
example, “available phosphorous”)
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Determination of soil pH (procedure)
• equipment : pH meter
• suspension soil/water or soil/dilute neutral salt (0.01M CaCl2 o 1M KCl)
• ratio soil to H2O (or salt solution) 1 :1 or 1: 2.5
• place 10 or 20 g of soil in a 50 or 100 ml beaker
• Add water or dilute neutral salt solution
• Swirl and let stand for an hour
• Insert the electrodes into the suspension (in the clear supernatant or in the sedimented soil) or the entire suspension may be stirred during the determination
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Particle-size analysis
• The aim of particle-size analysis is to split (in % or in g/kg) the elemental particles forming the fine earth in dimensional and conventional classes
• There are different classification systems, each of which uses specific dimensional classes
• Once a classification system is chosen, it is possible, by particle-size analysis, to determine the textural class of a soil
• The main classification systems are : – IUSS (ex ISSS) (International Union of Soil Society)
– USDA (United States Department of Agriculture)
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• The analysis may be performed with or without the removal of cementing agents
• The main cementing agents are:
– Organic matter
– Carbonate
– Iron oxides
– Soluble salts
• In any case, the sample is subjected to a dispersion procedure by dispersing agent (NaPO3)6
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The particle-size analysis is based on Stokes’ law
which describes the settling rate of a spherical
particle in a fluid.
• η = fluid viscosity
• h = distance covered
• g = acceleration due to gravity
• ρs = particle density
• ρl = fluid density
• η = viscosity fluid
• X = particle diameter
18
X)(gv
2
ls
2
lsX)(g
h18t
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• The most utilized methods are:
1. Pipette
2. Hydrometer
• Both the methods quantify the particles that did
not covered the distance h at fixed time
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Salinity
• The term salinity refers to the soluble plus
readily dissolvable salts in the soil
• Generally, in laboratory it is determined using an
aqueous extract of soil sample
• The soluble salt content can be evaluated from
measurement either of electrical conductivity
(EC) or of residue-weight upon evaporation to
dryness (TDS, total dissolved solids)
• The EC is the most utilized; it is determined on:
– an aqueous extract at fixed soil/water ratio (i.e. 1:2)
– an aqueous extract of so-called “saturated soil-paste”
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• The EC is measured in dS/m at 25°C by
• The saturation extract is better related to soil-water content under field conditions
• The negative effect of high amount of salts in the soil are: – Water stress caused by high osmotic potential of
soil liquid phase (mainly)
– Toxicity of the salts (secondly)
• For the compost, the EC is generally determined on an aqueous extract with ratio 1:10
• For the irrigation water the EC is directly measured on the sample
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Total Carbonate
• Inorganic carbonates in soil occurs predominantly
as calcite (CaCO3) and dolomite ( CaMg(CO3)2 )
but in arid regions sodium carbonate and
magnesium carbonate are also common.
• The carbonate influences:
texture and aggregate stability of the soil
availability of phosphorus, iron and other
elements
pH
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• Soil carbonate is usually quantified by reaction
with an acid, in a closed system (called
“calcimeter”), to form CO2
CaCO3 + 2 H+ → Ca2+ + CO2 + H2O
• At constant temperature, the increase in
pressure is linearly related to the quantity of
carbonate presents in the sample
• The total carbonate is expressed as g/kg
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• In the field, it is possible to do an estimation of
carbonate amount, by adding a few drops of
diluted HCl to some grams of soil
• If the effervescence is:
slight, the amounts is none or very low
strong, the amount is medium
violent, the amount is high
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Dietrich-Fruhling Calcimeter
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Organic Matter
The organic matter is probably the most important component of soil that influences the fertility
Main effects of soil organic matter
• Source of nutrients
• Structure of soil
• Nutrient holding capacity (C.E.C.)
• Water holding capacity
• Biological fertility
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Determination of organic carbon
The most widely method used is “dichromate oxidation techniques”. It consists of an oxidation of organic carbon by treatment with a hot mixture of K2Cr2O7 and H2SO4 according to the equation:
2 Cr2O72- + 3 C + 16 H+ → 4 Cr3+ + 3 CO2 + 8 H2O
After the reaction, the excess of Cr2O72- is titrated
with FeSO4 according to:
2 Cr2O72- + 6 Fe2+ + 14 H+ → 4 Cr3+ + 6 Fe3+ + 7 H2O
The titration occurs in presence of H3PO4 and diphenylamine (indicator)
Alternatively, in the titration, can be used o-phenanthroline without H3PO4
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The main methods adopted are:
• Walkley – Black (heat of dilution) for
soils in which the amount of organic
carbon does not exceed 8-10%
• Springer-Klee (external heat) for soils
with organic carbon content above 8-
10% and for organic fertilizers
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Total Nitrogen - I
• The routine method used for determination of
total N is the “Kjeldahl method” (1883) which is
essentially a wet oxidation procedure
• This procedure do not recover NO3-N, NO2-N
and some minor organic form; however, in
standard condition, all these form are present in
very small amount
• In Kjeldahl method, organic N in the sample is
converted to NH4+-N by digestion with
concentrated H2SO4 in presence of substances
promoting this conversion (1° step)
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• Then, the NH4+-N is determined from the amount of
NH3 liberated by distillation of the digest with alkali
(2°step)
• The speed and the completeness of conversion is
increased by adding salts to raise the temperature
of digestion (K2SO4), catalysts such as Cu (CuSO4)
and strong oxidizing agents such H2O2
• The NH3 liberated by distillation is collected into
boric acid (H3BO3) and then titrated with standard
H2SO4 or HCl
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• Neither the volume nor the strength of the
H3BO3 needs to be known accurately
because the ammonium borate formed is
titrated back to H3BO3
NH3 + H3BO3 → NH4+ + H2BO3
-
H+ + H2BO3- → H3BO3
• The total nitrogen is expressed as g/kg
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Total Nitrogen - II
• The total N can be also measured by “automatic
analyser” using a dry oxidation procedure
(Dumas method)
• This procedure recovers all N forms and
consists in a combustion at high temperature
(950 -1100 °C) with production of NOx
• Then, NOx are reduced to N2 and carried (by a
stream of He) to thermal cell for N measurement
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Soil phosphorus
• Phosphorus is a very important element for plant
nutrition
• It influences many biochemistry reaction in the
plants
• A want of P causes a poor fructification
• Phosphorus exists in soil as organic and
inorganic forms
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• Only a fraction of total phosphorus is available for
the plants
• For agronomic evaluation it is important to know
the “available phosphorus”
• To evaluate P availability, numerous soil tests
(availability indices) have been developed
• As availability indices, the main methods utilized
are:
Olsen, for neutral or alkaline soils (pH > 6)
Bray – Kurtz, for acid soils (pH < 6)
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• Olsen procedure utilizes a NaHCO3 solution as extractant
• Bray-Kurtz procedure uses a NH4F solution as extractant
• The extracted P is generally determined by colorimetric methods (blue Mo /SnCl2 or blue Mo/ascorbic acid) in which the blue intensity varies with the P concentration
• The blue intensity is measured by spectrophotometer UV-VIS using standard P solutions
• The P is expressed as mg/kg
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0
0.1
0.2
0.3
0 2 4 6 8 10 12 14
[ C ]
ABS
y = m x y = 0,018 x x = y/0,018
Calibration curve
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Exchangeable cations
• In the arid and semi-arid regions the main
exchangeable cations are:
– Ca
– K
– Mg
– Na
• K and Mg are very important for plant nutrition
• Ca and Na in excess can cause negative effects
• They are expressed as mg/kg or cmoli(+)/kg
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• The exchangeable cations are extracted by:
• NH4OAC solution (soils pH < 7)
• BaCl2 + TEA (Triethanolamine) solution buffered
at pH = 8.2 (soil pH > 7 )
• Cations in the extract can be determined by:
– Flame photometry (only Ca, K, Na)
– Atomic absorption
– ICP (Inductively Coupled Plasma)
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Heavy metals
• Cadmium (Cd)
• Nickel (Ni)
• Lead (Pb)
• Copper (Cu)
• Zinc (Zn)
• Mercury (Hg)
• Chromium (VI)
• Arsenic (As)
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Main chemical parameters for evaluation of
water quality for irrigation
• pH
• Electrical conductivity
• Sodium
• SAR index
• Chloride (Cl-)
• Hardness
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SAR INDEX
2
MgCa
NaSAR
22
2
MgCa
NaNadjSAR
22
X
Sodium
Adsorption
Ratio
New adjusted
Sodium
Adsorption
Ratio
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• Na, Ca, Mg
– Flame photometry (only Ca, Na)
– Atomic absorption
– ICP (Inductively Coupled Plasma)
– Titration (only Ca and Mg)
• Chloride (Cl-)
– Titration
– Ionic chromatography
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FAO limits for the evaluation
of water quality for irrigation
Restriction on use
None Slight to moderate Severe
Salinity ECw dS/m 25°C < 0.7 0.7 – 3.0 >3.0
Infiltration None Slight to moderate Severe
SAR 0-3 ECw >0.7 0.7-0.2 < 0.2
SAR 3-6 ECw > 1.2 1.2-0.3 < 0.3
SAR 6-12 ECw > 1.9 1.9-0.5 < 0.5
SAR 12-20 ECw > 2.9 2.9-1.3 < 1.3
SAR 20-40 ECw 5.0 5.0-2.9 < 2.9
Ion toxicity None Slight to moderate Severe
Na
Surface irrigation SAR < 3 3 - 9 > 9
Sprinkler irrigation me/l < 3 > 3
Cl -
Surface irrigation mg/l < 142 142 - 345 > 345
Sprinkler irrigation mg/l < 106 > 106
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