Environmental Chemistry and Analysis Prof. M.S.Subramanian Indian Institute of Technology Madras MODULE 2.2 Analysis of common ions at low concentrations in water Ultraviolet And Visible Spectrometry 1 Spectrophotometric instrumentation 2 Analysis by direct absorption 3 Nitrate determination 3 Analysis after formation of derivative 4 Chloride: Automated method using mercuric thiocyanate and ferric nitrate 4 Fluoride: Zr-Alizarin lake method 5 Nitrite 5 Phosphate 5 Automatic procedures 5 Field Techniques 6 Flame photometry 6 Ion Chromatography 7 Examples Of The Use Of Other Techniques 11 Ammonia 12 Fluoride 13 Sulphate 13 Free chlorine (Residual chlorine) 14 Sulphide 14 Sample Collection and preservation 15 Spectrophotometric determination of H 2 S 15 Titrimetric method 15 Cyanide 16
17
Embed
Analysis of common ions at low concentrations in water - NPTel
This document is posted to help you gain knowledge. Please leave a comment to let me know what you think about it! Share it to your friends and learn new things together.
Transcript
Environmental Chemistry and Analysis Prof. M.S.Subramanian
Indian Institute of Technology Madras
MODULE 2.2
Analysis of common ions at low concentrations in water Ultraviolet And Visible Spectrometry 1 Spectrophotometric instrumentation 2 Analysis by direct absorption 3 Nitrate determination 3
Analysis after formation of derivative 4 Chloride: Automated method using
mercuric thiocyanate and ferric nitrate 4
Fluoride: Zr-Alizarin lake method 5
Nitrite 5
Phosphate 5
Automatic procedures 5
Field Techniques 6
Flame photometry 6
Ion Chromatography 7
Examples Of The Use Of Other Techniques 11 Ammonia 12
Fluoride 13
Sulphate 13
Free chlorine (Residual chlorine) 14
Sulphide 14
Sample Collection and preservation 15
Spectrophotometric determination of H2S 15 Titrimetric method 15 Cyanide 16
Environmental Chemistry and Analysis Prof. M.S.Subramanian
Indian Institute of Technology Madras
MODULE 2.2
Analysis of common ions at low concentrations in water:
In this chapter the application of instrumental techniques to determine the
concentration of ions which are present in mg l -1 concentration range are
discussed . One of the major advantages of the use of instrumental techniques is
that elaborate sample preparation is not necessary. However when it comes to
the analysis of ions at µg l-1 levels, a preconcentration step is needed inorder to
bring the concentration of the analyte ions within the working range of the
instruments. In that case the instrumental part becomes just one part of a more
complex analytical procedure. The analysis of ions present at µg l-1 concentration
level are discussed in the next chapter.
Ultraviolet And Visible Spectrometry:
This technique is based on Beer-Lambert law. That is at sufficiently low
concentrations of the absorbing species the above law is obeyed which can be
expressed mathematically as
A = clε
Where A = absorbance of radiation at a particular wavelength;
o
t
IA logI
⎛ ⎞=⎜ ⎟
⎝ ⎠
= Intensity of incident radiation;
= Intensity of transmitted radiation;
= Molar absorptivity; l mol
oI
tI
ε -1 cm-1
1
Environmental Chemistry and Analysis Prof. M.S.Subramanian
Indian Institute of Technology Madras
C = Concentration of absorbing species (mol l -1);
l = Path length of light beam (cm)
There are many instruments which are used to measure the absorption of
light. These can range from sophisticated laboratory instruments which can
operate over the whole visible-ultraviolet range to portable colorimeters using
natural visible light, which are used as field instruments.
Natural water is colourless since none of the common ions present in
water absorb light in the visible region. The only ions which absorb in the
ultraviolet range above 200nm are nitrate and nitrite.
Since nitrate ions absorb at 220nm, it permits the concentrations of these
ions in water to be determined using spectrophotometer by direct absorption.
The concentration of ions such as chloride, fluoride and phosphate which
do not absorb in the visible region, can however be determined after converting
them into a suitable coloured species by chemical reactions. Nitrate and nitrite
also are converted into suitable coloured products, the absorbances of which can
be measured.
Spectrophotometric instrumentation:
The out line of a simple single-beam spectrophotometer is shown in fig.1.
Source Monochro mator
Sample Detector& read out
fig.1 block diagram of a single beam spectrophotomer
2
Environmental Chemistry and Analysis Prof. M.S.Subramanian
Indian Institute of Technology Madras
For absorption in the visible region, a tungsten lamp is used as a source and
that for absorption in uv region hydrogen lamp is used. The light of the desired
wavelength is isolated using diffraction monochromator. Normally for all
absorption measurements 1 cm cells are used and for all uv absorption
measurements cells made of quartz are used. Different types of detectors such
as photocell, photomultiplier or photodiode array detectors are used in the
absorption measurements.
Analysis by direct absorption:
Nitrate determination:
This method is useful only for screening water samples that have low
organic matter contents, i.e., uncontaminated natural waters and potable water
supplies.The calibration curve follows Beer's law upto 11
ppm. Measurement of uv absorption at 220nm enables rapid determination of
nitrate. Because dissolved organic matter also may absorb at 220 nm and
does not absorb at 275 nm, a second measurement made at 275 nm, may
be used to correct the value. The extent of this empirical correction is
related to the nature and concentration of organic matter and may vary from one
water to another. This method is therefore not recommended if a significant
correction for organic matter absorbance is required, although it may be useful in
monitoring levels within a water body with a constant type of organic
matter. Sample filtration is intended to remove possible interference from
suspended particles. Acidification with 1N HCl is designed to prevent interference
from hydroxide or carbonate concentration upto 1000 ppm as CaCO
-3NO
-3NO
-3NO
-3NO
3. Chloride
does not interfere in the determination. However organic dissolved matter,
surfactant, , and Cr(VI) do interfere. -2NO
3
Environmental Chemistry and Analysis Prof. M.S.Subramanian
Indian Institute of Technology Madras
Analysis after formation of derivative:
Chloride: Automated method using mercuric thiocyanate and ferric nitrate:
Thiocyanate ion is liberated from mercuric thiocyanate solution by the
formation of soluble mercuric chloride. In the presence of ferric ion, free
thiocyanate ion, forms a highly coloured ferric thiocyanate complex
(λmax=470 nm) the absorbance of which is proportional to the chloride
concentration.
The interference due to particulate matter can be overcome by filtration or
centrifugation before analysis.
The method is applicable to potable, surface, and saline waters, and
domestic and industrial waste waters. The concentration range of chloride that
can be measured is 1 to 200 ppm.
Fluoride: Zr-Alizarin lake method:
This SPANDS Colorimetric method is based on the reaction
between fluoride and a coloured zirconium-alizarine lake. Fluoride reacts with the
Zirconium alizarin lake, dissociating a portion of it into a colourless complex
anion (ZrF62-). As the amount of fluoride increases, the colour of zirconium dye
lake becomes progressively lighter.
The reaction between fluoride and zirconium ions is influenced
greatly by the acidity of the reaction mixture. If the proportion of acid in the
reagent is increased, the reaction can be made almost instantaneous. The
absorbance measurements can be done at 570nm and concentrations can be
4
Environmental Chemistry and Analysis Prof. M.S.Subramanian
Indian Institute of Technology Madras
determined with calibration graph. Both the standards and samples should be
kept for one hour before absorption measurements.
Nitrite:
Nitrite is determined through formation of a purple azo dye produced
at pH 2.0 to 2.5 by coupling diazotised sulfanilamide with
N-(1-naphthyl)-ethylenediaminedihydrochloride. The absorbance of the resulting
purple azo dye can be measured at 543 nm using a spectrophotometer. Beer's
law is obeyed upto 25 µg
-2NO
-1. Higher Concentration of can be determined by
diluting the sample. Free chorine and the following ions which form precipitates
under test conditions such as Sb
-2NO
3+ ,Au3+, Bi3+, Fe3+, Pb2+, Hg2+, Ag+ interfere .
Cupric ion may cause low results by catalysing decomposition of the diazonium
salt.
Phosphate: The procedure for phosphate involves the addition of a mixed