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These techniques are closely related to colorimetry
Both the techniques are based on the scattering of light by non transparent particles in a suspended in a solution.
The two techniques differs only in the manner of measuring the scattered radiation
When the light is allowed to pass through a suspension, the part of the incident radiant energy is dissipated by absorption,reflection,and refraction while the remainder is transmitted.
Tyndall effect
Light scattering by particles in a colloid or particles in a fine suspension.
the longer-wavelength light is more transmitted while the shorter-wavelength light is more reflected via scattering.
PRINCIPLE
NEPHELOMETRY
measurement of the light scattered by suspended particles at right angles(900) (perpendicular) to the incident beam.
TURBIDIMETRY
measurement of the light transmitted by suspended particles to the incident beam.
TURBIDIMETRY & COLORIMETRY
Measurement of the intensity of light transmitted through a medium
Light intensity is decreased
NEPHELOMETRY & FLUORIMETRY
Measurement of scattered light at 900
both incident & scattered light are same wavelength -NEPHELOMETRY
scattered light wavelength is longer than the incident light - FLUORIMETRY
CHOICE OF THE METHOD
depends upon the amount of light scattered by suspended particles present in solution.
TURBIDIMETRY - high concn. Suspensions
NEPHELOMETRY – low concn. Suspensions
more accurate results
THEORY
REFLECTION VS SCATTERING
If the dimensions of the suspended particles larger than the wave length of the incident light - REFLECTION
If the dimensions of the suspended particles smaller(same order) than the wave length of the incident light - SCATTERING
NEPHELOMETRY
suspended particles < incident light wave length :
smaller particles undergo scattering – secondary rays - maximum intensity at 900
- most of the instruments measured at this angle
suspended particles > incident light wave length :larger particles undergo reflection – small fraction of light get deviated maximum intensity at < 900
5-200 / 450
NEPHELOMETRY
suspended particles should neither be too large nor too small otherwise the scattering efficiency falls off.
optimum particle size should be 0.1- 1 micro meters.
TURBIDIMETRY
suspended particles > incident light wave length :
larger particles undergo reflection- measuring transmitted radiation
larger particles- absorbance vs concn – not linear
measurements can not be accurate
Factors affecting measurements
The amount of radiation removed or deviated from the primary radiation beam depends on the following factors
A.Concentration:
TURBIDIMETRY
IT=Transmittance = Io
Beer’s law
Io S = log = kbc I
S= turbidence due to scatteringK = proportionality constant / Turbidity constantb = path lengthC = concentration of suspended material
NEPHELOMETRY
Is = Ks Io c
Is = scattered intensity
Ks = empirical constant
Io = incident intensity
c = concentration of the scattered material
Working curve
C Vs Is / Io
log Io / Is Vs C
B.Particle geometry
Control of particle size & shape - most critical factor
Same distribution
Conditions – concn. Of reactants,
temp,
agitation,
pH,
order of mixing,
time allowed for particle growth
C.Incident light wave length
TURBIDIMETRY
It is an imp factor
Select a wave length- sample solution does not absorb strongly
If the sample solution is colorless – use the incident light of the same color
If clear solutions having dark particles – light in red / IR
NEPHELOMETRY
Absorption is much less- white light is generally used
D.Refractve index difference
Appreciable RI differences between particles & surrounding medium – best results
Change solvents in order to increase the RI differences
INSTRUMENTATION
SOURCES
FILTERS/MONOCHROMATORS
CELLS
DETECTORS
SOURCES
White light – nephelometers
Mercury arc
Tungsten lamp
FILTERS / MONOCHROMATORS
mono chromatic radiation
CELLS
cylindrical cells - flat faces
to minimize reflections & multiple scatterings
cell with a rectangular cross section is preferred
semi octagonal faces
octagonal faces- 00,450,900,1350
NEPHELOMETER
light source
sensitive micro-ammeter
Filter wheel with a series of colour filters
annular photocell
reflector to collect the scattered light
test tube
metal test tube cover to exclude extraneous light.
The test solution (sample) is placed in a test tube (F) that has been duly rested on a light source (A)
The scattered light caused by the particles in a turbid or cloudy solution is immediately directed by the reflector (E) on to an annular photocell (D).
A series of standard colour filters are usually provided in the form of a filter-wheel (C) so as to facilitate analysis of coloured solutions ;
Taking care that the filter chosen must be similar to colour to that of the solution.
The current generated after passing through the photocell (i.e., light energy is being converted to electrical energy) is recorded by a sensitive micro-ammeter (B).
The test tube is provided with a metallic cover (G) to get rid of any extraneous light.
Usually a nephelometer is provided with zero-setting controls, sensitivity adjusting device and a set of previously matched test tubes.
TURBIDIMETER
Either visual or photoelectric colorimeters may be satisfactorily employed as turbidimeters.
However, the use of the blue filter normally enhances the sensitivity appreciably.
It has been observed that the light transmitted by a turbid solution does not normally obey the Beer-Lambert Law accurately and precisely.
Therefore, as an usual practice it is advisable to construct a ‘calibration curve’ by employing several standard solutions.
The concentration of the unknown solution may be read off directly from the above calibration curve as is done in the case of colorimetric assays
APPLICATIONS