Chapter
1:
Fluorescence Theory
Chapter
2:
Advantages of Fluorescence
Chapter
3:
Instrumentation
Chapter
4:
Variables of Fluorescence
Chapter
5:
Calibration and Standards
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An
Introduction to
Fluorescence
Measurements
Chapter 4
- Variables of Fluorescence
4.1 Linearity, Quenching, Turbidity,
Bubbles in the Sample, pH, and Photochemical Decay.
4.11 Linearity.
Fluorescence intensity is typically directly proportional (linear) to
concentration. There are, however, factors that affect this linear relationship.
When concentration is too high, light cannot pass through the sample
to cause excitation; thus very high concentrations can have very low
fluorescence (concentration quenching; see section 4.12). At intermediate
concentrations, the surface portion of sample nearest the light absorbs
so much light that little is available for the rest of the sample; thus
the readings will not be linear, though they will be within the range
of a calibration curve.[18] See Figure 6.[19]
The linearity of a sample is related
to many factors, including the chemical composition of the sample and
the pathlength the light must travel (thus, the diameter of the cuvette
or sample holder is a factor). An unknown sample should always be tested
for linearity. Because instrument factors also affect linearity, samples
must be tested on the specific instrument to be used in the study; if
cuvette size is changed or optical filters are changed to different
wavelengths, linearity must be tested. To test for linearity, simply
take a reading for a high concentration of the sample; dilute by a factor
(1:1, 1:10, etc.); and take a reading for the dilute sample. If it is
linear, the reading will go down by the same factor as the dilution.
If it is non-linear, the reading will most likely increase as it is
diluted. If it is in the range for a calibration curve, the reading
will go down, but not as much as expected by the dilution. Although
a calibration curve for a specific application may prove to be non-linear,
if the curve is reproducibly accurate, then the calibration is accurate.
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Figure 6.
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For example, Rhodamine WT, a fluorescent
tracer widely used in environmental studies, is linear to about 100
parts per billion (ppb) active ingredient using the Turner Designs 10-AU-005-CE
fluorometer with the 25 mm cuvette. It is in the range for a calibration
curve to about 500 ppb active ingredient.
4.12 Quenching. The
term "quenching" refers to many factors that reduce, or quench
fluorescence. Quenching as it relates to linearity is discussed in section
4.11. Temperature quenching is discussed in section 4.2. Factors that
influence quenching can be controlled through instrument design and
proper method development. For more details on quenching, click
here.
Quenching factors are one reason why
it is very important to treat standards, blanks, and samples in exactly
the same manner. Thus, for the best accuracy, prepare all solutions
in the same manner, using the same reagents and matrix solution and
the same preparation techniques; measure at the same temperature after
the same amount of time. Good laboratory techniques will go a long way
toward producing reliable results.
4.13 Turbidity.
Fluorescence measurements are significantly more immune to the effects
of turbidity compared to absorption techniques like UV/VIS spectrophotometers.
Turbidity is often viewed as an impurity or background in a solution
(i.e., suspended solid like silt). If the interfering substance is reflective,
turbidity can create light scatter and readings will increase. If the
interfering substance absorbs light, fluorescence will be reduced. If
the interfering substance does not absorb light, however, then the fluorescence
readings will not be effected unless there is so much turbidity that
the emitted light cannot penetrate the water. In extreme cases of turbidity,
samples can be filtered to minimize these effects. For various applications,
turbidity can easily be corrected for in the field.[21] Keep in mind
that these interferences can in effect be "canceled out" by
using the same matrix water for standards, blanks, and samples and treating
them exactly in the same manner.
4.14 Bubbles in the Sample. Since
fluorescence is such a sensitive measurement, and since accuracy of
readings depend on light exciting the molecules of the compound, bubbles
in the sample can result in erratic or fluctuating readings. In cuvettes,
if bubbles are suspected, wait for them to settle. In continuous flow
systems, take care not to introduce bubbles by avoiding turbulent waters
and water too near the pump; or employ a filtering system or bubble
trap. Sample intake should be through the bottom and outflow through
the top. In a falling stream flow cell, bubbles are not an issue as
they are part of the background measurement.
4.15 pH.
Fluorescence can be affected by pH. Yet, in field studies of water,
this is rarely an issue. Where it is an issue, the usual rule applies:
use the same matrix water for standards, blanks, and samples and treat
them in exactly the same manner. If working with pH-dependent solutions,
read solutions at different pHs to determine affects on fluorescence.
In certain studies, pH factors can be
an advantage. Spectral interferences can be minimized in analytical
fluorescence spectrometry by adjustment of pH prior to measurement.
The pH dependence of probe molecules has been used to determine the
pH of intact and cured cells.[22]
4.16 Photochemical Decay.
Many fluorescent molecules can be bleached or destroyed by light (fading
of dyes in the sun). Ultraviolet light, especially, can cause certain
molecules to break down. Fluorescence readings decrease as the molecules
are destroyed. Rate of destruction varies depending upon environmental
factors, including temperature. Fluorescein, for example, is destroyed
rapidly in sunlight. Rhodamine WT, however, is adequately stable for
field studies.[23] For chlorophyll measurements, samples and standards
need to be kept in the dark until read. All flow measurements should
employ opaque delivery hose to minimize photochemical interferences.
Glass provides shielding from laboratory light and ultraviolet light;
the extent of shielding varies depending on the type of glass.
4.2 Temperature
Fluorescence is affected by changes in
temperature. As temperature increases, fluorescence decreases. Guilbault
suggests that this is due to an increase of molecular motion with increasing
temperature, which results in more molecular collisions and subsequent
loss of energy.[24] The temperature coefficient varies depending upon
the compound being measured. Using a filter fluorometer, this problem
is easily resolved by measuring standards, blanks, and samples at the
same temperature. For flow through studies, the researcher can set up
a system to measure the temperature of samples, then compensate readings
later using a spreadsheet program. Some field fluorometers like the
Turner Designs 10-AU-005-CE offer a temperature compensation option,
where the fluorometer measures sample temperature, then automatically
compensates readings for changes in temperature.
4.3 Cuvette Size (Pathlength); Flow Cell
Fouling
4.31 Cuvette Size.
Linearity and detection limits are affected by cuvette size (pathlength).
In general, the greater the diameter of the cuvette, the lower the upper
end of the linear range, and the lower the limits of detection. For
example, using the Turner Designs 10-AU-005-CE with the 25 mm cuvette,
Rhodamine WT is linear to 100 ppb with detection limits in the range
of 0.01 ppb in DI water. When the 13 mm cuvette is used, Rhodamine WT
is linear to 400 ppb with detection limits of 0.04 ppb in DI water.
The range of concentrations to be measured
and the detection limits can be optimized by selecting the appropriate
size cuvette. This can be especially effective for measuring substances
such as aromatic hydrocarbons. Readings can be obtained in the linear
range by the appropriate selection of cuvette diameter (3 mm for example)
and/or by offsetting the light path slightly or employing a light attenuator
(smaller window or slit).
Note that sample volume is not as important
as pathlength or diameter of the cuvette. Thus, for certain applications
like DNA quantitation where sample volumes are low, special low-volume
cuvettes with appropriate sample windows are available.
4.32 Flow Cell Fouling.
Fouling of the flow cell will result in lower, inaccurate readings over
time. This comes about when the glass or quartz cuvette becomes coated
as sample passes through. How long this takes depends on the quality
and temperature of the sample water. There are ways to minimize this
problem, including regular cleaning of the flow cell and recalibration
of the instrument; or employing a filtering system where biomass is
a problem. The Turner Designs TD-4100 employs a non-fouling, falling
stream detection system that does not use a glass flowcell, and therefore
does not require cleaning.
Continue...
to Chapter 5
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