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CHAPTER 4 NEW REAGENTS FOR THE...
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CHAPTER 4
NEW REAGENTS FOR THE SPECTROPHOTOMETRIC
DETERMINATION OF VANADIUM IN ALLOYS, SYNTHETIC AND
PHARMACEUTICAL SAMPLES
4.1 INTRODUCTION
4.2 ANALYTICAL CHEMISTRY
4.3 APPARATUS
4.4 REAGENTS AND SOLUTIONS
4.5 PROCEDURES
4.6 RESULTS AND DISCUSSION
4.7 APPLICATIONS
4.8 CONCLUSIONS
4.9 REFERENCES
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4.1 INTRODUCTION
Vanadium is an essential trace element to man and animals. It was first
discovered by del Rio in 1801 [1-3]. Unfortunately, a French chemist incorrectly
declared Del Rio's new element as only impure chromium and Del Rio thought
himself to be mistaken and accepted the French chemist's statement. The element was
rediscovered in 1830 by Sefstrom, who named the element in honor of the
Scandinavian Goddess Vanadis because of its beautiful multicolored compounds. It
was isolated in nearly pure form by Roscoe in 1867. Vanadium of 99.3 to 99.8 %
purity was not produced until 1922.
Vanadium has abundance in the earth’s crust of about 0.02 %. Vanadium is
found in about 65 different minerals among which carnotite, roscoelite, vanadinite
and patronite are the important sources of the metal [4]. Vanadium is also found in
phosphate rock and certain iron ores, and is present in some crude oils in the form of
organic complexes. It is also found in small percentages in meteorites. High-purity
ductile vanadium can be obtained by the reduction of vanadium trichloride with
magnesium or with magnesium-sodium mixtures. Much of the vanadium being
produced are now made by calcium reduction of V2O5 in a pressure vessel, an
adaptation of a process developed by McKechnie and Seybair. Natural vanadium is a
mixture of two isotopes, 50V (0.24 %) and 51V (99.76 %). 50V is slightly radioactive,
having a half-life of > 3.9×1017 years. Nine other unstable isotopes are recognized.
Pure vanadium is a bright white metal and is soft and ductile. It has good corrosion
resistance to alkalies, sulfuric and hydrochloric acid and salt water, but the metal
oxidizes readily above 660 0C. The metal has good structural strength and a low
fission neutron cross section, making it useful in nuclear applications. Vanadium is
used in producing rust resistant spring, and high speed tool steels. It is an important
carbide stabilizer in making steels. About 80 % of the vanadium now produced is
used as ferrovanadium or as a steel additive. Vanadium foil is used as a bonding agent
in cladding titanium to steel. Vanadium pentoxide is used in ceramics and as a
catalyst. It is also used in producing a superconductive magnet with a field of 175,000
gauss. Vanadium and its compounds are toxic and should be handled with care.
Ductile vanadium is commercially available and commercial vanadium metal of about
95 % purity.
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Major sources for the emission of vanadium in the environment include
combustion of fuel oils, dyeing, ceramics, ink, catalyst and steel manufacturing.
Vanadium in trace amounts represents an essential element for normal cell growth,
but it can be toxic when present in higher concentrations. It plays an important role in
physiological systems including normalization of sugar levels and participation in
various enzyme systems as an inhibitor and cofactor of the oxidation of amines [5].
In spite of being a nutritional element, vanadium is not accumulated by the biota. The
only organisms known to bio-accumulate it to any significant degree are some
mushrooms, tunicates and sea squirts. The occurrence of vanadium in sea squirts is
supposed to be one of the main sources of this metal in crude oil and oil shales.
In biology, vanadium ion is an essential component of some enzymes,
particularly the vanadium nitrogenase used by some nitrogen fixing microorganisms.
Vanadium is essential to sea squirts in vanadium chromagen proteins. The
concentration of vanadium in their blood is more than 100 times higher than the
concentration of vanadium in the seawater around them. Rats and chickens are also
known to require vanadium in very small amounts and deficiencies result in reduced
growth and impaired reproduction. Administration of oxovanadium compounds have
been shown to alleviate diabetes mellitus symptoms in certain animal models and
humans. Much like the chromium effect on sugar metabolism, the mechanism of this
effect is unknown.
Vanadium poisoning is an industrial hazard [6]. Environmental scientists have
declared vanadium as a potentially dangerous chemical pollutant that can play havoc
with the productivity of plants, crops and the entire agricultural system. High amounts
of vanadium are said to be present in fossil fuels such as crude petroleum, fuel oils,
coals and lignite. Burning of these fuels release vanadium into the air that then settle
on the soil. Vanadium compounds act chiefly as an irritant to the eyes and respiratory
tract. Exposure may cause conjunctivitis, rhinitis and reversible irritation of the
respiratory tract. More severe cases may cause bronchitis, bronchospasms and asthma
like disease. It may cause polycythemia, red blood cell destruction and anemia,
albuminuria and hematuria, gastrointestinal disorders, nervous complaints and severe
cough [7]. Recently, vanadium has been noticed as the index element in urban
environmental pollution, especially air pollution [8]. Laboratory and epidemiological
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evidences suggest that vanadium may also play a beneficial role in the prevention of
heart disease [9]. Shamberger has pointed out that human heart disease death rate is
lower in countries where more vanadium occurs in the environment [10]. The
National Institute for Occupational Safety and Health (NIOSH) has recommended that
35 mgm-3 of vanadium be considered immediately dangerous to life and health. This
is the exposure level of a chemical that is likely to cause permanent health problems
or death.
The determination of vanadium provides significant information regarding its
biological effects and the extent of air pollution. Soldi et al. reported that this element
was a useful marker for the potential release of toxic metals from fossil fuels,
especially oils, as it is always present in these materials [11]. Thus, highly and
selective methods are still required for trace vanadium determination in different
kinds of samples.
4.2 ANALYTICAL CHEMISTRY
Several methods have been reported in the literature for the analysis of
vanadium. Various analytical techniques based on fluorescence spectroscopy [12],
atomic absorption spectroscopy [13], inductively coupled plasma-atomic absorption
spectroscopy [14], capillary electrophoresis [15], stripping voltametry [16], neutron
activation analysis [17], high-performance liquid chromatography [18] and ion
exchange separation method [19] are used for its determination.
A survey of literature revealed that a large number of reagents are suitable for
the spectrophotometric determination of vanadium. Telep and Boltz reported
hydrogen peroxide as a reagent for the spectrophotometric determination of vanadium
[20]. The method was based on the reaction of vanadium(V) with H2O2 in acid
medium to form a reddish-brown colored complex. The complex showed maximum
absorption at 290 nm. Beer's law was valid over the concentration range 0-125 ppm of
vanadium. Eeckhout and Weynants reported diphenylbenzidine as a reagent for the
determination of vanadium [21]. The yellow color resulted from the reaction between
dilute solution of V(V) and diphenylbenzidine was the basis for the
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spectrophotometric method for the determination of vanadium. Beer's law was valid
over the concentration range 1-�������-1 of vanadium.
Motojima reported oxine as a reagent for the spectrophotometric
determination of vanadium [22]. This method was based on the extraction of
vanadium-oxine complex with chloroform and the complex exhibited an absorption
maximum at 550 nm. Baggett and Huyck reported spectrochemical determination of
vanadium in alkali brines [23]. In this method samples were adjusted to a pH value of
5.0, treated with 8-quinolino1 and quinolates extracted with chloroform. The
chloroform extract was concentrated by evaporation to a known volume and placed on
a graphite electrode previously coated with 20% sodium hydroxide and dried in an
oven with a carbon dioxide atmosphere. Excitation was carried out by a 2300 volt
alternating current arc with photographic recording of the spectra and molybdenum
was used as the internal standard.
Jones and Watkinson described a spectrophotometric method for the
determination of vanadium in plant materials [24]. With minor modifications it was
used to determine vanadium in soils. Priyadarshini and Tandon reported N-benzoyl-
N-phenylhydroxylamine as a reagent for the spectrophotometric determination of
vanadium [25]. Ariel and Manka reported a spectrophotometric method for the
determination of chromium(VI) and vanadium(V) [26]. The presence of iron(III) was
developed by exploiting the color changes which resulted from the oxidation of
o-dianisidine in strong acid medium.
Shibata described a solvent extraction and spectrophotometric determination
of vanadium with 1-(2-pyridylazo)-2-naphthol [27]. Janauer et al. reported a sensitive
and precise spectrophotometric method for the determination of microgram quantities
of vanadium in hydrochloric acid-methanol medium [28]. The photometric reagent
was the azo dyestuff solochrome black-RN, which formed a violet colored complex
with vanadium, which showed maximum extinction at 560 nm. Beer's law obeyed
within the concentration range from 0 to 25 �g of vanadium per 10 ml of test solution.
Sailendra Nath and Poddar described spectrophotometric determination of vanadium
with o-hydroxyacetophenone oxime as a reagent [29,30]. Reagents like
p-methoxybenzothiohydroxamic acid [31], 2-(2-thiazolylazo)-5-(diethylamino)phenol
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[32] and morin [33] were also used as reagents for the spectrophotometric
determination of vanadium. Gagliardi and Ilmaier described a sensitive method for the
spectrophotometric determination of vanadium with 4-(2-pyridylazo)resorcinol(PAR)
[34]. The method was applicable to the analysis of alloys.
Goyal and Tandon described the comparative studies of the reaction of 7-
arylazo-8-hydroxyquinoline-5-sulphonic acid (Azoxine S) dye with vanadium, which
showed that 2:1 yellow, water-soluble complex formed over the pH range 2.5–6.0 and
the phenyl derivative was the most suitable for spectrophotometric determination of
0.2–1.4 ppm of vanadium [35]. The color formed instantaneously and was stable for
about 8 hours. The molar abso�� ���� ��� �max =400 was 1.15×104� ��� ���� ����
equilibrium constant for complex formation was of the order of 102. These dyes were
used as indicators in the direct complexometric determination of vanadium(IV). The
interference of a number of anions and cations were reported. Tamotsu et al. reported
protocatechuic acid as a spectrophotometric reagent for the determination of
vanadium [36].
Tandon and Bhattacharya used N-aryl hydroxamic acid as a reagent for the
spectrophotometric determination determination of vanadium [37]. Wakamatsu and
Otomo described an extraction and spectrophotometric determination of
vanadium(IV) with Tiron [38]. The vanadium(IV)-Tiron chelate was extracted into a
mixed solvent mixture 1:4, isopentyl alcohol:chloroform in the presence of
1,3-diphenylguanidinium salt. Beer’s law was obeyed upto 36 ���vanadium per 10
mL of the solvent.
Chakraborti reported 3-hydroxy-1,3-diphenyltriazene and its substituted
derivatives as spectrophotometric reagents for vanadium(V) [39]. Izquierdo and
Lacort described 5,7-dichloro-2-methyl-8-hydroxy-quinoline as a reagent for the
vanadium determination by spectrophotometry [40]. Satyanarayana and Mishra
reported 1,2,3-phenyloxyamidine as a reagent for solvent extraction and
spectrophotometric determination of vanadium(V) [41]. The course of investigations
on the development of organic analytical reagents were able to introduce a type of
functional group for metal ions. 1,2,3-Phenyloxyamidine possessed several useful
properties as an analytical reagent. It was stable and can be readily prepared from
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common laboratory chemicals. The reagent has great potentialities for the
colorimetric and gravimetric determination of metal ions. Studies carried out in these
laboratories showed that this was an excellent reagent for the spectrophotometric
determination of vanadium(V) by solvent extraction and for the gravimetric
determination of copper and nickel with the functional group.
Naoichi et al. described a spectrophotometric determination of vanadium(V)
with N-benzoyl-N-phenylhydroxylamine [42]. Vojkovic et al. reported the application
of 1-phenyl-2-methyl-3-hydroxy-4-pyridone (HX) for the spectrophotometric
determination of vanadium(V) by extraction into chloroform [43]. The method was
based on the extraction condition and three types of complexes were formed. At pH
1.0-2.2, an orange colored complex of the composition with a maximum absorption at
497 nm was formed. However, at 0.75-1.25 M hydrogen ion concentration and in the
presence of the excess of chloride ions a blue colored complex of the composition
VO2Cl(HX)2 with a maximum absorption at 625 nm was found. In the presence of an
excess perchlorate ions and at 0.3-0.4 M hydrogen ion concentration a blue colored
complex of composition VO2ClO4(HX)3 with a maximum absorption at 605 nm was
established. The latter complex was not recommended for the determination as an
excess of perchlorate influenced the absorption. Procedures for the determination at
497 or 625 nm were very fast and simple. The complexes were also isolated in
crystalline form and identified by elemental analysis and infrared spectroscopy. The
molar absorptivity at 497 nm was 4100 Lmol-1cm-1 and at 625 nm 5600 Lmol-1cm-1.
Uchida et al. reported a spectrophotometric determination of vanadium(V)
with 2-nitroso-5-dimethylaminophenol [44]. Nardillo and Catoggio described a
spectrophotometric determination of vanadium with 3-methyl catechol in alloy steels
[45]. Reagents like 1-(4-tolyl)-2-methyl-3-hydroxy-4-pyridone [46], 4-(4,5-dimethyl-
2-thiazolylazo)-2-methylresorcinol [47] and N-methylaminothioformyl-N'-
phenylhydroxylamine [48] were used for the spectrophotometric determination of
vanadium.
Akama et al. described a spectrophotometric determination of vanadium(V)
using 4-benzoyl-3-methyl-1-phenyl-5-pyrazolone [49]. Bag et al. reported
spectrophotometric method for the determination of vanadium with
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2:2′-diaminodiphenyldisulphide in strong acidic solution [50]. Vanadium(V) formed a
1:1 cornflower blue colored complex with 2:2′-diaminodiphenyldisulphide in 18 N
sulfuric acid solution which passed onto 1:2 complex with large amount of reagent.
The absorption maxima of the complexes were 590 nm and 700 nm respectively. The
Beer’s law was obeyed in the concentration range 8-36 ppm. The percent relative
error was 2.72. The composition of the complexes were determined by the modified
jobs and molar ratio method. The calculated dissociation constants were 1.6×10–2 and
5×10–9 at 25 °C. The molar extinction coefficient was 1100, while the Sandell’s
sensitivity was 0.046 μgcm-2.
Reddy and Reddy reported extraction and spectrophotometric determination of
vanadium [51]. In this method vanadium(V) formed a 1:1 yellow colored complex
with salicylaldehyde thiosemicarbazone in n-butanol. The yellow colored complex
was quantitatively extracted from acetic acid medium into n-butanol. Beers law was
obeyed in the range 0.5-6.5 ppm of the metal. Large number of foreign ions did not
interfere.
Montelongo et al. reported a spectrophotometric determination of
vanadium(V) with 4-(1��-1�������-triazolyl-3�-azo)-2-methylresorcinol [52]. The
method was based on the reaction of vanadium with the reagent at pH 8.10
(Tris-HClO4 buffer solution), produced a pink-violet, 1:1 complex (λmax=525 nm,
ε=2.55×104 Lmol–1cm–1) in a 50% methanol-water medium, which was the basis for
the spectrophotometric determination of 0.1 to 1.51 ppm of vanadium. The method
was applied for the determination of the vanadium content in low alloy steels.
Salinas and Arrabal described a method for the extract and spectrophotometric
determination of vanadium(V) [53]. The violet colored complex formed with
isophthaldihydroxamic acid was extracted into trioctylmethylammonium chloride in
ethylacetate (λmax=380 nm, ε=7.50×103 Lmol–1cm–1; λmax=510 nm, ε=5.51×103
Lmol–1 cm–1) and the range of the determination was 14-80 μg.
Escriche et al. reported a spectrophotometric method for the determination of
vanadium [54]. The method was based on the oxidation of pyrogallol red and
vanadium was determined by the decrease in absorbance of its characteristic band at
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490 nm and at pH 4. The decrease in absorbance was proportional to the
concentration of vanadium(V) over the range 0–1.83 ppm. The limit of detection of
vanadium was found to be 0.05 ppm. In the presence of potassium bromate the
determination was possible in the ppb levels. The method described the study of the
selectivity of the method with respect to possible interference from 20 species
contained in ferrous and non-ferrous alloys, which was classified according to their
possible mechanism of interference.
Abdullah et al. reported thiophene-2-hydrazide as a reagent for the
spectrophotometric determination of trace amount of vanadium in aqueous solution
[55]. The intense yellow, water-soluble, stable and binary complex formed in acidic
medium was used for the determination of 0.5–5 ppm of vanadium ion with a molar
absorptivity of 12.1×103 Lmol–1cm–1 at 410 nm. Moreover, the color formation was
very fast. Interferences due to foreign ions were examined.
El-Shahat et al. reported phenylfluorone as a reagent for the
spectrophotometric determination of vanadium [56]. The method was based on the
formation of a 1:1 complex of vanadium - phenylfluorone exhibited an absorption
maximum at 520 nm. The Beer's law was valid over the concentration range of 2-15
μg of vanadium in 10 mL at pH 4. The relative standard deviation was 2 % and the
molar absorptivity of the system was 2.1×104 Lmol-1cm-1.
Bhaskar and Surekha reported 2-acetylpyridine thiosemicarbazone as a reagent
for the spectrophotometric determination of vanadium [57]. Vanadium formed a
golden yellow complex at pH 3.5 with 2-acetylpyridine thiosemicarbazone in aqueous
medium. The complex exhibited maximum absorbance at 400 nm, with molar
absorptivity of 5.6×103 Lmol-1cm-1. The metal and ligand stoichiometric ratio was 1:1
and the Beer's law was valid over the concentration range 0-8 ppm of vanadium.
Svjetlana and Vladimir reported desferrioxamine-B as a reagent for the
determination of vanadium [58]. A naturally occurring trihydroxamic acid,
desferrioxamine-B, reacted with the vanadium(V) ion in strong acidic aqueous
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solution and produced a stable 1:1 complex. This red-violet chelate used for the
spectrophotometric determination of trace amounts of vanadium(V). Molar
absorptivity of the system was 3.15×103 Lmol-1cm-1 and Beer's law was valid over the
vanadium concentration range 0.5-50 ppm.
Krasiejko and Marczenko presented a sensitive and highly selective method
for the spectrophotometric determination of microgram amounts of vanadium(V) [59].
First, vanadium was isolated by extraction with N-benzoyl-N-phenylhydroxylamine
(BPHA) in chloroform from 4 M hydrochloric acid medium. Then, chloroform was
evaporated and the residue mineralized with mixture of concentrated perchloric and
nitric acid. Finally, a color reaction of vanadium(V) separated with 2-(5-bromo-2-
pyridylazo)-5-diethylaminophenol (5-Br-PADAP) in an acetate buffer (pH 4.5). The
molar absorptivity of the method was 5.48×104 Lmol–1cm–1 at 585 nm. The proposed
method was applied for the determination of traces of vanadium in aluminium
samples. The results obtained showed a good precision and accuracy of the method.
Eshwar and Sharma used 1-(2'-thiazolylazo)-2-naphthol as reagent for the
extractive spectrophotometric determination of vanadium in high speed steel [60].
The sparingly soluble complex formed between vanadium(V) and 4-(2-thiazolylazo)
resorcinol was extracted with chloroform. The complex exhibited an absorption
maximum at 610 nm with molar absorptivity 1.50×104 Lmol-1cm-1. Beer's law was
valid over the concentration range 0.08-2.24 ����-1 of vanadium.
Marczenko and Lobinski described an extraction and spectrophotometric
determination of trace amounts of vanadium with 3,5-dinitrocatechol(DNC) and
brilliant green(BG) [61]. Beer's law was obeyed up to a vanadium concentration of
0.3� ����-1 and the molar absorptivity was 1.7×105 Lmole��cm�� at 630 nm. The
molar ratios of the components and the form of the vanadium(V) cation in the
extracted compound was determined and the formula [VO(OH)(DNC)2�2][BG+]2 was
proposed. Titanium, molybdenum, tungsten, EDTA and thiocyanate interfered
seriously. The proposed method has been applied to determination of traces of
vanadium (about 10��� %) in alums. Mandelohydroxamic acid [62], alizarine
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complexone and cetylpyridinium halides [63] were also reported as reagents for the
determination of vanadium in steels.
Kshatriya and Basant developed a selective and sensitive method for the
spectrophotometric determination of vanadium(V) in biological materials with
N-benzylpalmito hydroxamic acid (BPHA) [64]. Vanadium(V) was extracted with
BPHA into chloroform at 3-7 M HCl. The reagent reacted with vanadium to form a
reddish-violet complex with molar absorptivity of 3.79×103 Lmol-1cm-1 at 500 nm.
Beer's Law was obeyed in the concentraction range of 2-8 ppm vanadium.
Aman et al. reported an improved spectrophotometric determination of
vanadium using benzidine-phosphoric acid [65]. Vanadium reacted with benzidine in
acidic medium, which formed a pink colored complex showed maximum absorbance
at 520 nm. The method was successfully applied to the determination of vanadium in
thermal gas turbine deposits and fuel oil sludge.
Yang et al. reported diantipyryl-(3, 4-dioxymethenyl) phenylmethane as a
reagent for the determination of vanadium in herbal medicine [66]. Molar absorptivity
of the system was 3.21×105 Lmol-1cm-1 at 470 nm. Beer's law was obeyed in the range
of 0.2-���������� ����� ����������������!�" ���#��������$�#��% &%��� �����$���$�
acids [67] were also reported as reagents for the determination of vanadium in
pharmaceutical and steel samples.
Biao and Rong reported chlorpromazine as a sensitive reagent for the
determination of vanadium [68]. Chlorpromazine reacted with vanadium(V) at room
temperature to form a bright red complex, which exhibited an absorption maximum at
520 nm. Beer's law was obeyed in the concentration range of 2-��������� ����� �����
10 mL with molar absorptivity of 5.10×103 Lmol-1cm-1.
Costa et al. reported a simple and sensitive spectrophotometric method for the
determination of vanadium(IV) using 2-(5-bromo-2-pyridylazo)-5-
diethylaminophenol (Br-PADAP) [69]. The method was based on the oxidation of
vanadium(IV) to vanadium(V) by the addition of iron(III) cation, followed by a
complexation reaction of iron(II) with a spectrophotometric reagent (Br-PADAP).
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The iron(II) reacted with Br-PADAP which formed a stable complex with a large
molar absorptivity. The vanadium(IV) determination was possible, with a calibration
sensitivity of 0.549 ������ for an analytical curve of 18.8 ngm1-1� ��������������,
molar absorptivity of 2.80×104 Lmol-1cm-1 and a detection limit of 5.5 ngm1-1. The
proposed method was applied for the vanadium(IV) determination in the presence of
several amounts of vanadium(V'��(��� �% #�%� � ��#��� ����� ���������� ����� �)*'�
�������� ��������+������������������������������� ����� �),*'��(����$�%��������
the accuracy obtained were satisfactory (R.S.D. < 2%). Reagents such as N-
phenylcinnamohydroxamic acid and azide [70], 2'-hydroxyacetophenone
benzoylhydrazone [71,72] were also reported for the spectrophotometric
determination of vanadium.
Ahmed and Banoo developed a sensitive, fairly selective direct
spectrophotometric method for the determination of trace amount of vanadium(V)
with 1,5-diphenylcarbohydrazide [73]. The reagent 1,5-diphenylcarbohydrazide
(DPCH) reacted in slightly acidic (0.0001–0.001 M H2SO4 or pH 4.0–5.5) 50%
acetone media with vanadium(V) to give a red–violet chelate which showed
maximum absorption at 531 nm. The average molar absorption coefficient and
Sandell’s sensitivity were found to be 4.23×104 Lmol��cm�� and 10 ngcm�� of
vanadium respectively. Linear calibration graph were obtained for 0.1–��������� of
vanadium. The stoichiometric composition of the chelate was 1:3 (V:DPCH). The
reaction was instantaneous and absorbance remain stable for 48 h. The interference
����� �����$�����%�������%�����$��#�!���������%���%�&����%� ���������������� of
vanadium. The method was successfully used in the determination of vanadium in
several standard reference materials (alloys and steels), environmental waters (potable
and polluted), biological samples (human blood and urine), soil samples, solution
containing both vanadium(V) and vanadium(IV) and complex synthetic mixtures. The
���������%�������$�%���������$$ �$��)%-�.������������������).
Agnihotri et al. reported a highly sensitive and selective spectrophotometric
determination of vanadium(V) using 6-chloro-3-hydroxy-7-methyl-2-(2-thienyl)-4H-
chromen-4-one as a complexing agent in a weakly acidified (HCl, pH 0.84–1.09)
medium [74]. The greenish-yellow complex was quantitatively extracted into carbon
tetrachloride and showed maximum absorbance at 417–425 nm. The method obeys
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/��0%� #�+� ��� ��1� ������� of vanadium having molar absorptivity and Sandell’s
sensitivity of 8.26×104 Lmol-1cm-1����������2���$��� of vanadium respectively. The
method applied to the determination of vanadium in steels, reverberatory flue dust and
water samples. 6-Chloro-3-hydroxy-2-[2'-(5'-methylfuryl)]-4H-chromen-4-one used
as a reagent for the determination of vanadium in various synthetic samples [75].
Vanadium reacted with 6-chloro-3-hydroxy-2-[2'-(5'-methylfuryl)]-4H-chromen-4-
one, which formed a dark yellow (1:1) colored species exhibited an absorption
maximum at 432 nm. Beer's law was valid over the concentration range 0.2-1.4
����-1 of vanadium. Molar absorptivity and Sandell's sensitivity of the system was
3.98×104 Lmol-1cm-1��������������$�-2 respectively. The reagents 5,7-dichlorooxine,
rhodamine-6G [76] and isothipendyl hydrochloride [77] were also used and reported
for the determination of vanadium in steels and minerals.
Mohamed and Fawy reported a catalytic spectrophotometric method for the
determination of vanadium in seawater samples [78]. The method was based on the
catalytic effect of vanadium on the bromate oxidative coupling reaction of metol with
2,3,4-trihydroxybenzoic acid (THBA). The optimum reaction conditions are 6.4×10-3
M of metol, 2.0×10-3 M of THBA and 0.16 M of bromate at 35º C and in the presence
of an activator-buffer solution of 1.0×10-2 M of tartarate (pH=3.10). The reagent
phenothiazine derivatives were also reported for the determination of vanadium in
steels, minerals, biological samples and soil samples [79].
Di et al. reported a spectrophotometric method for the determination of
vanadium(V) based on the formation of tungstovanadophosphate-3,3',5,5'-
tetramethylbenzidine-N-propanesulfonic (TMBPS) charge transfer complex [80]. The
spectrophotometric measurements were directly carried out at 450 nm and the
apparent molar absorptivity was 2.74×104 Lmol-1cm-1. The linear range of the
determination was 0.02-1.0 �����1. The sensitivity was enhanced with a flotation-
extraction preconcentration method and the apparent molar absorptivity was 3.10×105
Lmol-1cm-1.
Dian-Wen and Li-Xian reported arsenazo-M as a reagent for the determination
of vanadium in iron ores [81]. This method was based on decolorizing reaction of
arsenazo-M by vanadium(V) in H2SO4 medium. The decrease in color was directly
proportional to the amounts of vanadium. The maximum absorption was at 547 nm
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and the molar absorption coefficient was 1.04×103 Lmol-1cm-1. Beer’s law was valid
over the concentration range 0-���������� ����� �������������3����-Hua et al. used
2-(5-carboxy-1,3,4-triazolylazo)-5-diethylamino benzoic acid [82] as a reagent for the
spectrophotometric determination of vanadium in an aluminium alloy sample.
Agnihotri et al. reported 2,4-dihydroxyacetetophenonebenzoylhydrazone
(DABH) and pyridine as reagents for the spectrophotometric determination of
vanadium in variety of synthetic samples [83]. The method was based on the
formation of light brown complex of vanadium with 2,4-dihydroxyacetophenone
benzoylhydrazone and pyridine. The molar absorptivity and relative standard
deviation of the method was 2.83×104 Lmol-1cm-1 and 0.19 % for vanadium
$��$��������� ���� ����-1 respectively. Beer's law was valid over the vanadium
concentration range 0-��������-1. 2-(2-Quinolylazo)-5-diethylaminophenol was also
used as spectrophotometric reagent for the determination of vanadium in water and
biological samples [84].
Cherian and Narayana reported a simple and sensitive spectrophotometric
method for the determination of trace amounts of vanadium using thionin as a
chromogenic reagent [85]. The method was based on the reaction of vanadium(V)
with potassium iodide in acidic medium to liberate iodine. Bleaching of the violet
color of thionin by the liberation of iodine was the basis of the determination and was
measured at 600 nm. Beer's law was obeyed over the range of 0.2-��� ����-1 of
vanadium. The molar absorptivity, Sandell's sensitivity, detection limit and
quantitation limit of the method were found to be 2.298×104 Lmol-1cm-1, 0.520×10-2
��$�-2������������-1 �������������-1 respectively. The method was applied to the
analysis of vanadium in synthetic and alloy samples.
Kiran Kumar and Revanasiddappa reported variamine blue as a reagent for the
spectrophotometric determination of trace amounts of vanadium [86]. The method
was based on the oxidation of variamine blue to a violet colored species on reaction
with vanadium(V), having an absorption maximum at 570 nm. Beer’s law was obeyed
in the range of 0.1-2.0 ����-1. The molar absorptivity and Sandell’s sensitivity were
found to be 1.65×104 Lmol-1cm-1� ������������$�-2 respectively. Optimum reaction
conditions were evaluated in order to delimit the linear range. The effect of interfering
99
ions on the determination was described. The proposed method was successfully
applied to the determination of vanadium in steel, pharmaceutical, environmental and
biological samples.
Mastoi et al. developed a spectrophotometric method for the determination of
vanadium with 2-pyrrolealdehyde phenylsemicarbazone (PPS) [87]. The linear
calibration curve was obtained with 2.5-20 ����-1 of vanadium. Copper(II),
cobalt(II), iron(II) and palladium(II) were also determined separately using PPS with
linear calibration curves within 2.5-12.5, 5-15, 2.5-15 and 1-������-1 at 362, 355,
355 and 365 nm, respectively. The vanadium in crude oil was determined with
relative standard deviation of 2.5-5.0%. The method has been applied for the analysis
of copper from copper wires, cobalt from pharmaceutical preparation and palladium
from palladium on barium sulphate with RSD within 2.6-4.5%.
Sao et al. reported a reagent system using rhodamine-B dye for the
determination of vanadium [88]. The method was based on the reaction of vanadium
with acidified potassium iodide to liberate iodine. Bleaching of the pink color of
rhodamine-B by the liberation of iodine was the basis of the determination and was
measured at 553 nm. Beer's law was obeyed over the concentration range of 2-�2����
of vanadium in final solution volume of 25 mL (0.08-0.64 ppm). The apparent molar
absorptivity and Sandell's sensitivity were found to be 1.3×105 Lmol-1cm-1 and 0.0009
��$�-2 respectively. The method was simple, sensitive and satisfactorily applied to
ppm level for the determination of vanadium in different environmental and
biological samples.
Qi-Li and De-Yun described a simple and highly sensitive spectrophotometric
method for the determination of vanadium(V) [89]. The method was based on
catalytic oxidation of 1,8-dihydroxynaphthalene-3,6-disulfonic acid and
phenylhydrazine with potassium chlorate. The molar absorptivity was 7.8×106 at the
wavelength of 506 nm, detection range was 0.2-5.0 ngmL-1. It was successfully
applied to the determination of trace amounts of vanadium in spring water, black
bean, corn, tea leaves, and rhodiola schalinensis A leaves.
100
Xianzhong and Yun developed a spectrophotometric determination of
vanadium in carbonaceous shales (stone coal ores) [90]. The method was based on the
reaction of vanadium(V) with the chromophore reagent 2-(5-bromo-2-pyridylazo)-5-
diethylaminophenol (5-Br-PADAP) in the presence of hydrogen peroxide. In a 0.072
M sulfuric acid medium, 5-Br-PADAP reacted with vanadium(V) to form a red-violet
complex with maximum absorption peak at 596 nm with an apparent molar absorption
coefficient of the complex of 8.45×104 Lmol��cm��. Beer's law was obeyed in the
range 0–��� ��� ����� �� ��� ��� ��� ��� %�# ������ +���� �� $��#������ $�����$����� ���
0.9995. Interferences due to various non-target ions were also investigated and high
quantities of other common inorganic ions were tolerable. The method involved the
dissolution of the ore sample by Na2O2 fusion, followed by filtering of the alkali
solution after which Fe(III), Cu(II), Ni(II) and Co(II) etc. were effectively separated
from the solution by precipitation in a NaOH solution. Selectivity was increased with
the use of EDTA as a masking agent. The vanadium in ore sample was determined
with a relative deviation (RSD) between 0.20 and 0.76 %, and has been successfully
applied to the determination of vanadium-bearing stone coal ores. The results
indicated that the accuracy of 5-Br-PADAP spectrophotometry was comparable with
the ICP-AES method.
Kumar et al. developed a facile, sensitive, selective and rapid
spectrophotometric method for the determination of trace amounts of vanadium(V) in
various samples [91]. The method was based on the interactions of
3-methyl-2-benzothiazolinone hydrazone hydrochloride (MBTH) with N-(1-naphthyl)
ethylenediamine dihydrochloride (NEDA) in the presence of vanadium formed a blue
colored derivative or on oxidation of dopamine hydrochloride (DPH) by vanadium in
acidic medium and coupling with MBTH, yielded pink colored derivative. The blue
colored derivative having an absorbance maximum at 595 nm was stable for 9 days
and the pink colored derivative with maximum absorption 526 nm was stable for 5
days. Beer’s law was obeyed for vanadium in the concentration range 0.05–6.0 ����-
1 (blue color derivative) and 0.06–7.0 ����-1 (pink color derivative), respectively.
The optimum reaction conditions and other important analytical parameters were
established. Interference due to various non-target ions was also investigated. The
proposed methods were applied to the analysis of vanadium(V) in environmental,
biological, pharmaceutical and steel samples.
101
Kumar et al. described a simultaneous second-derivative spectrophotometric
determination of cobalt and vanadium using 2-hydroxy-3-methoxybenzaldehyde
thiosemicarbazone (HMBT) [92]. HMBT reacted with Co(II) and vanadium(V) at pH
6.0 formed green-colored complexes in aqueous dimethyl formamide. The second
derivative spectrum of Co(II) complex showed a zero amplitude at 434.5 nm and a
large amplitude at 409.5 nm, while the V(V) complex showed a sufficient amplitude
at 434.5 nm and a zero amplitude at 409.5 nm. The derivative amplitudes obeyed
Beer’s law at 409.5 and 434.5 nm for Co(II) and V(V) in the range 0.059–3.535 and
0.051–���4�� ����-1 respectively. This enabled the simultaneous determination of
Co(II) and V(V) without separation. Foreign ions did not interfere in the present
method. The method was applied to the simultaneous determination of Co(II) and
V(V) in synthetic mixtures and alloy steel samples. However, most of the reported
methods suffer from a number of limitations, such as interference by a large number
of ions, low sensitivity and need extraction into organic solvents. Therefore a simple
and reliable spectrophotometric method for the determination of vanadium is clearly
recognized.
The present work is to develop a simple spectrophotometric method for the
determination of vanadium using toluidine blue, safranine O and leuco xylene cyanol
FF. The developed method has been successfully applied to the analysis of the
vanadium in alloys, synthetic and pharmaceutical samples.
102
4.3 APPARATUS
A Secomam Anthelie NUA 022 UV-Visible spectrophotometer with 1 cm
quartz cell was used. A WTW pH 330 pH meter was used.
4.4 REAGENTS AND SOLUTIONS
All chemicals were of analytical reagent grade or chemically pure grade and
distilled water was used throughout the study. Vanadium stock solution
(1000 μgmL-1) was prepared by dissolving 0.2395 g of Na3VO4 in 100 mL of water
and standardized volumetrically [93]. The following reagents were prepared by
dissolving appropriate amounts of reagents in distilled water. Toluidine blue (0.05 %),
safranine O (0.1 %), leuco xylene cyanol FF (0.1 %) (0.1 g of xylene cyanol FF was
dissolved in 25 mL of water containing 30 mg of zinc dust and 2 mL of 1 M acetic
acid, stirred well and kept aside for 20 minutes. The resulting solution was then
diluted to 100 mL with water), hydrochloric acid (2 M), potassium iodide (2 %),
sodium acetate solution (1 M) and sulfuric acid (0.05 M).
4.5 PROCEDURES
4.5.1 Using Toluidine Blue as a Reagent
Aliquots of sample solution containing 0.4–8.0 μgmL-1 of vanadium solution
were transferred into a series of 10 mL calibrated flasks. A volume of 1 mL of 2 %
potassium iodide solution was added followed by 1 mL of 2 M hydrochloric acid and
the mixture was gently shaken until the appearance of yellow color, indicating the
liberation of iodine. A 0.5 mL of 0.05 % toluidine blue solution was then added to it
followed by the addition of 2 mL of 1 M sodium acetate solution and the reaction
mixture shaken for 2 minutes. The contents were diluted to 10 mL with distilled water
and mixed well. The absorbance of the resulting solutions were measured at 628 nm
against the corresponding reagent blank. A reagent blank was prepared by replacing
the analyte(vanadium) solution with distilled water. The absorbance corresponding to
the bleached color which in turn corresponds to the analyte(vanadium) concentration
was obtained by subtracting the absorbance of the blank solution from that of test
103
solution. The amount of the vanadium present in the volume taken was computed
from the calibration graph (Figure IVB1).
4.5.2 Using Safranine O as a Reagent
Aliquots of sample solution containing 0.5–12.4 μgmL-1 of vanadium were
transferred into a series of 10 mL calibrated flasks. A volume of 1 mL of 2 %
potassium iodide solution was added followed by 1 mL of 2 M hydrochloric acid and
the mixture was gently shaken until the appearance of yellow color, indicating the
liberation of iodine. A 0.5 mL of 0.1 % safranine O solution was then added to it
followed by the addition of 2 mL of 1 M sodium acetate solution and the reaction
mixture shaken for 2 minutes. The contents were diluted to 10 mL with distilled water
and mixed well. The absorbance of the resulting solutions were measured at 530 nm
against the corresponding reagent blank. A reagent blank was prepared by replacing
the analyte(vanadium) solution with distilled water. The absorbance corresponding to
the bleached color which in turn corresponds to the analyte(vanadium ) concentration
was obtained by subtracting the absorbance of the blank solution from that of test
solution. The amount of the vanadium present in the volume taken was computed
from the calibration graph (Figure IVB2).
4.5.3 Using Leuco Xylene Cyanol FF as a Reagent (LXCFF)
Aliquots of sample solution containing 0.05–8.0 μgmL-1 of vanadium were
transferred into a series of 10 mL calibrated flasks. Then, volumes of 0.5 mL of the
0.05 M H2SO4 and 0.7 mL of the 0.1% LXCFF were added and the mixture was kept
on a water bath (≈90°C) for 15 minutes, after being cooled to room temperature
(27 ± 2°C), the contents were diluted to the mark with sodium acetate buffer of pH 4,
and mixed well. The absorbance of the xylene cyanol FF dye formed was then
measured at 614 nm against the reagent blank prepared in the same manner, without
vanadium. The amount of the vanadium present in the volume taken was computed
from the calibration graph (Figure IVB3).
4.5.4 Determination of Vanadium(V) in Vanadium Steel and Synthetic Mixtures An accurately weighed amount of vanadium steel (~0.5 g) was treated with 15
mL of concentrated sulfuric acid and 1 mL of concentrated nitric acid and the solution
104
boiled gently to dissolve the sample. The oxides of nitrogen formed were expelled,
the solution was cooled and diluted to 50 mL with double distilled water. Chromium
was extracted with 5 mL of methyl isobutyl ketone [88]. A 0.01 M solution of
potassium permanganate was added dropwise until the solution appeared pink. The
solution was allowed to stand for 5 minutes, warmed and 0.05 M oxalic acid solution
added slowly with stirring until the pink color of the solution was discharged. The
solution was diluted to 100 mL with distilled water. Using the suitable aliquot of the
solution vanadium content was determined using the proposed procedure.
Synthetic mixtures were prepared by mixing exact concentration of different
metal ions keeping the composition of the synthetic mixture as constant and 1 mL of
this sample solution was used for the determination of vanadium(V) according to the
procedure described above. The results are listed in Table 4B1, 4B2, 4B3, 4C1, 4C2
and 4C3.
4.5.5 Determination of Vanadium(V) in Pharmaceutical Sample
A volume of 10 mL of neogadine elixir (Raptakos Brett & Co. Ltd. Mumbai,
India) sample was treated with 10 mL of concentrated HNO3 and the mixture was
then evaporated to dryness. The residue was leached with 5 mL of 0.5 M H2SO4. The
solution was diluted to a known volume with water after neutralizing with dilute
ammonia. An aliquot of the made up solution was analysed for vanadium according to
the general procedure for vanadium determination. The results are listed in Table
4D1.
4.6 RESULTS AND DISCUSSION
4.6.1 Absorption Spectra
4.6.1.1 Using toluidine blue as a reagent
This method involves the liberation of iodine by the reaction of vanadate with
potassium iodide in an acidic medium. The liberated iodine bleaches the blue color of
toluidine blue and absorbance of the solution is measured at 628 nm. This decrease in
absorbance is directly proportional to the vanadium concentration. The absorption
spectrum of colored species of toluidine blue is presented in Figure IVA1 and reaction
system is presented in Scheme IV.
105
4.6.1.2 Using safranine O as a reagentThis method involves the liberation of iodine by the reaction of vanadate with
potassium iodide in an acidic medium. The liberated iodine bleaches the pinkish red
color of safranine O and absorbance of the solution is measured at 530 nm. This
decrease in absorbance is directly proportional to the vanadium concentration. The
absorption spectrum of colored species of safranine O is presented in Figure IVA2
and reaction system is presented in Scheme IV.
4.6.1.3 Using leuco xylene cyanol FF as a reagent In this method vanadium quantitatively oxidize leuco xylene cyanol FF into
its blue colored xylene cyanol FF dye in a sulfuric acid medium ( pH 1.4-3.9 ) on a
boiling water bath (∼90°C for 15 minutes); the resulting colored dye shows a
maximum absorbance at 614 nm in an acetate buffer medium ( pH 4.0-4.5 ). The
reagent blank have negligible absorbance at this wavelength. The absorption spectra
of the colored species of LXCFF are presented in Figure IVA3 and reaction system is
presented in Scheme IV.
4.6.2 Effect of the Reagent Concentration and Acidity
4.6.2.1 Using toluidine blue and safranine O as reagents
The effect of iodide concentration and acidity on the reaction system is studied
with 2 μgmL-1 vanadium. The oxidation of iodide to iodine by vanadium is effective
in the pH range 1.0-1.5, which can be maintained by adding 1 mL of 2 M HCl in a
final volume of 10 mL. The liberation of iodine from potassium iodide in an acidic
medium is quantitative. It is found that 1 mL of 2 % KI and 1 mL of 2 M HCl are
sufficient for the liberation of iodine from iodide by vanadium. A 0.5 mL of each
0.05 % toluidine blue and 0.1% safranine O is used for subsequent decolorization.
Constant and maximum absorbance values are obtained in the pH range of
4±0.2. Hence the pH of the reaction system is maintained at 4±0.2 throughout the
study. This can be achieved by the addition of 2 mL of 1 M acetate buffer solution in
a total volume of 10 mL. The maximum absorbance is obtained instantaneously and
requires no heating under the reaction conditions. Under the optimum reaction
106
conditions, toluidine blue and safranine O reaction systems are found to be stable for
a period of 4 hours.
4.6.2.2 Using leuco xylene cyanol FF as a reagent
The oxidation of LXCFF by vanadium is studied. Of the various acids
(sulfuric acid, hydrochloric acid and phosphoric acid) studied, sulfuric acid is found to
be the best acid for the system. Constant absorbance readings are obtained in the 0.1-
1.5 mL range of 0.05 M sulfuric acid (or pH 1.4-3.9) at a temperature 90°C for 15
minutes. An increase of the pH above 3.9 markedly affected the stability and
sensitivity of the dye. Color development did not take place below pH 1.4. Hence a
volume of 0.5 mL of 0.05 M sulfuric acid (or maintained pH=2) in a total volume of
10 mL is used in all subsequent work.
The optimum concentration of LXCFF leading to maximum color stability is
found to be 0.7 mL of 0.1 % reagent per 10 mL of the reaction mixture. The
absorbance values are measured in the pH range of 3.5-4.0. This can be achieved by
adding 3 mL of acetate buffer of pH=4. Appreciable results are obtained when the
entire reaction mixture is diluted with the same acetate buffer solution of pH=4. A
change in the pH of the final reaction mixture is affected by the intensity of the
colored dye. The formed colored dye is stable for more than 24 hours.
4.6.3 Analytical Data
4.6.3.1 Using toluidine blue as a reagentThe adherence to Beer’s law is studied by measuring the absorbance values of
solutions varying vanadium concentration. A straight line graph is obtained by
plotting absorbance against concentration of vanadium. Beer’s law is obeyed in the
range of 0.4–8.0 μgmL–1 of vanadium (Figure IVB1). The molar absorptivity and
Sandell’s sensitivity of the system is found to be 2.141×104 Lmol-1cm-1 and 2.36×10-3
μgcm-2 respectively. Correlation coefficient (n=10) and slope of the calibration curve
are 0.995 and 0.141 respectively. The detection limit (DL=3.3σ/s) and quantitation
limit (QL=10σ/s) [where σ is the standard deviation of the reagent blank (n=5) and s is
the slope of the calibration curve] of vanadium determination are found to be 0.234
μgmL-1 and 0.709 μgmL-1 respectively.
107
4.6.3.2 Using safranine O as a reagentAdherence to Beer’s law is studied by measuring the absorbance values of
solutions varying vanadium concentration. A straight line graph is obtained by
plotting absorbance against concentration of vanadium. Beer’s law is obeyed in the
range of 0.5–12.4 μgmL-1 of vanadium (Figure IVB2). The molar absorptivity and
Sandell’s sensitivity of the system is found to be 3.06×104 Lmol-1cm-1, 1.66×10-3
μgcm-2 respectively. Correlation coefficient (n = 10) and slope of the calibration
curve are 0.997 and 0.144 respectively. The detection limit (DL=3.3σ/s) and
quantitation limit (QL=10σ/s) [where σ is the standard deviation of the reagent blank
(n=5) and s is the slope of the calibration- curve] for vanadium determination are
found to be 0.635 μgmL-1 and 1.920 μgmL-1 respectively.
4.6.3.3 Using leuco xylene cyanol FF as a reagent
Adherence to Beer’s law is studied by measuring the absorbance values of
solutions varying vanadium concentration. A straight line graph is obtained by
plotting absorbance against concentration of vanadium. Beer’s law is obeyed in the
range of 0.05–8.0 μgmL-1 of vanadium (Figure IVB3). The molar absorptivity and
Sandell’s sensitivity of the colored system is found to be 1.16×104 Lmol-1cm –1 and
4.38×10-3 ��$�-2 respectively. The detection limit (DL=3.3 σ/s) and quantitaion limit
(QL=10 σ/s) [where σ is the standard deviation of the reagent blank (n=5) and s is
the slope of the calibration- curve] for vanadium determination are found to be 0.027
μgmL-1 and 0.08 μgmL-1 respectively.
4.6.4 Effect of Divers IonsThe effect of various ions at microgram levels on the determination of
vanadium is examined. The tolerance limits of the interfering species are established
at those concentrations, which caused not more than ±2.0 % changes in the
absorbance value during the determination of a fixed amount of vanadium (2 μgmL-1).
The tolerance limits of the foreign ions are given in Table 4A1 and 4A2. In this
reaction system, various oxidants such as Cu2+, Cr6+, Fe3+, iodate and periodate
interfered. Interference of chromium can be removed by extracting with 5 mL methyl
isobutyl ketone [94]. Iron and copper can be masked with sodium fluoride and 2-
108
mercaptoethanol respectively. However, the tolerance level of other ions may be
increased by the addition of 1 mL of 1 % EDTA.
4.7 APPLICATIONS
The developed method is applied to the quantitative determination of
vanadium in alloys, synthetic and pharmaceutical samples, the results are summarized
in Table 4B1, 4B2, 4B3, 4C1, 4C2, 4C3 and 4D1 respectively. The precision of the
proposed method is evaluated by replicate analysis of samples containing vanadium at
five different concentrations.
4.8 CONCLUSIONS
1. The reagents provide simple method for the spectrophotometric determination of
vanadium.
2. The developed method does not involve any extraction step and hence the use of
organic solvents, which are generally toxic are avoided.
3. The developed method does not involve any stringent reaction conditions and
offers the advantages of high stability of the reaction system for toluidine blue
(more than 4 hours), safranne O (more than 5 hours) and leuco xylene cyanol FF
(more than 24 hours).
5. The developed method has been successfully applied to the analysis of the
vanadium in alloy samples, synthetic mixtures and pharmaceutical samples. A
comparison of the method reported is made with earlier methods and is given in
Table 4D2.
109
FIGURE IVA1 ABSORPTION SPECTRUM OF COLORED SPECIES OF TOLUIDINE BLUE
Wavelength (nm)
200 300 400 500 600 700 800 900
Abs
orba
nce
0.0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
FIGURE IVA2
ABSORPTION SPECTRUM OF COLORED SPECIES OF SAFRANINE O
Wavelength (nm)
200 300 400 500 600 700 800
Abs
orba
nce
0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
1.6
1.8
110
FIGURE IVA3ABSORPTION SPECTRA OF COLORED SPECIES OF LEUCO XYLENE
CYANOL FF Vs REAGENT BLANK (a) AND REAGENT BLANK Vs DISTILLED
WATER (b)
Wavelength (nm)
300 400 500 600 700 800 900
Abs
orba
nce
0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
a
b
FIGURE IVB1
ADHERANCE TO BEER’S LAW FOR THE DETERMINATION OF VANADIUM
USING TOLUIDINE BLUE AS A REAGENT
C oncen tra tion o f vanad ium (µgm L -1)
0 2 4 6 8 10 12
Ab
sorb
an
ce
0 .0
0 .2
0 .4
0 .6
0 .8
1 .0
1 .2
111
FIGURE IVB2 ADHERANCE TO BEER’S LAW FOR THE DETERMINATION OF VANADIUM
USING SAFRANINE O AS A REAGENT
Concentration of vanadium (µgm L-1)
0 2 4 6 8 10 12 14 16
Abs
orba
nce
0 .0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
FIGURE IVB3
ADHERANCE TO BEER’S LAW FOR THE DETERMINATION OF VANADIUM
USING LEUCO XYLENE CYANOL FF AS A REAGENT
C oncentration of Vanadium (µgm L -1)
0 2 4 6 8 10 12 14
Abs
orba
nce
0 .0
0.5
1.0
1.5
2.0
2.5
112
SCHEME IV
2 VO43- + 12 H+ + 2 I - 2 VO2+ + I2 + 6 H2O
N
S+
CH3
NH2(CH3)2N
NH
S
CH3
NH2(CH3)2N
I2 , H+
Toluidine Blue(Colored) Toluidine Blue(Colorless)
N
N+
CH3
NH2NH2
CH3 NH
N
CH3
NH2NH2
CH3 I2 , H+
Safranine O(Colored) Safranine O(Colorless)
NH
CH3
CH3 CH3
NH
CH3
SO3H
SO3Na
H + V5+
NH
CH3
CH3 CH3
N
CH3
SO3H
SO3Na
+ V4+
Xylene Cyanol FF (Colorless) Xylene Cyanol FF (Colored)
113
TABLE 4A1 EFFECT OF DIVERSE IONS ON THE DETERMINATION OF VANADIUM
(2 μgmL-1) USING TOLUIDINE BLUE AND SAFRANINE O
Foreignions
Tolerancelimit
����-1
Foreignions
Tolerancelimit
����-1
Fe3+ *
Ni2+
Cu2+ *
Cd2+
Bi3+
Al3+
Ca2+
Ba2+
In3+
Gd3+
Ti4+
Mo6+
105001550075050010001000750500500250
Cr6+ *
Mg2+
F-
PO43-
Iodate*
CitrateOxalateNitrate
02250100750< 4
15001500500
* Masked with masking agent
TABLE 4A2
EFFECT OF DIVERSE IONS ON THE DETERMINATION OF VANADIUM
(2 μgmL-1) USING LEUCO XYLENE CYANOL FF
Foreignions
Tolerancelimit
����-1
Foreignions
Tolerancelimit
����-1
Fe3+*
Ni2+
Cu2+
Cd2+
Na+
K+
Sm3+
Eu3+
Mg2+
Zn2+
Mn2+
Al3+
Ca2+
Co2+
≤ 1500200650200015001000500100025007506502000500
La3+
Cr2O72-*
F-
In3+
PO43-
Ti4+
Mo6+
Gd3+
OxalateAcetate
TartaratecitrateSulfateIodate*
Nitrate
500≤ 1100150050
10002501000150010002020
1000≤ 1
1500
* Masked with masking agent
114
TABLE 4B1
DETERMINATION OF VANADIUM IN VANADIUM STEELS USING
TOLUIDINE BLUE AS A REAGENT
Sample Composition%
% of vanadium present
% of vanadium
founda
Relativeerror (%)
Recovery(%)
1 C,0.56; Si, 0.24; Mn, 0.91; Ni, 0.23; Cr, 1.03; Mo, 0.04; V, 0.12, Cu, 0.19, P,0.022, S, 0.018
0.120
0.119 ±
0.015 -0.83 99.20
2 C,0.17; Si, 0.13; Mn, 0.53; Ni, 0.20; Cr, 0.20; Mo, 0.85 ; V, 0.28; Cu, 0.10; P,0.015; S, 0.025
0.280
0.278 ±
0.02 -0.71 99.30
a. Mean ± standard deviation (n = 5)
Cu is masked using 2-mercaptoethanol.
TABLE 4B2
DETERMINATION OF VANADIUM IN VANADIUM STEELS USING
SAFRANINE O AS A REAGENT
Sample Composition%
% of vanadium present
% of vanadium
founda
Relativeerror (%)
Recovery(%)
1 C,0.56; Si, 0.24; Mn, 0.91; Ni, 0.23; Cr, 1.03; Mo, 0.04; V, 0.12, Cu, 0.19, P,0.022, S, 0.018
0.120
0.118 ±
0.02 -0.83 99.20
2 C,0.17; Si, 0.13; Mn, 0.53; Ni, 0.20; Cr, 0.20; Mo, 0.85 ; V, 0.28; Cu, 0.10; P,0.015; S, 0.025
0.280
0.279 ±
0.01 -0.36 99.30
a. Mean ± standard deviation (n = 5)
Cu is masked using 2-mercaptoethanol.
115
TABLE 4B3
DETERMINATION OF VANADIUM IN VANADIUM STEELS USING LEUCO
XYLENE CYANOL FF AS A REAGENT
Sample Composition %
% of vanadium present
% of vanadium founda
Relativeerror (%)
Recovery(%)
1 C,0.56; Si, 0.24; Mn, 0.91; Ni, 0.23; Cr, 1.03; Mo, 0.04; V, 0.12, Cu, 0.19, P,0.022, S, 0.018
0.120
0.122 ±
0.06 +1.66 101.66
2 C,0.17; Si, 0.13; Mn, 0.53; Ni, 0.20; Cr, 0.20; Mo, 0.85 ; V, 0.28; Cu, 0.10; P,0.015; S, 0.025
0.280
0.274 ±
0.02 -2.14 97.85
a. Mean ± standard deviation (n = 5)
Cu is masked using 2-mercaptoethanol.
TABLE 4C1
DETERMINATION OF VANADIUM IN SOME SYNTHETIC MIXTURES USING
TOLUIDINE BLUE AS A REAGENT
Sample Compositions of m�!� ��)����-1) *����� �)*'�)����-1) Recovery Added Founda ±SD (% )
1 Zn2+ (25)+Cd2+ (25) 1.00 1.01±0.03 101.0
2 Zn2+ (25)+Cd2+ (25)+CrVI (5)+Mn2+ (20) 0.50 0.49±0.03 98.0
3. Zn2+ (25)+Cd2+ (25)+CrVI (5)+Mn2+ (20) 0.50 0.52±0.50 104.0
+Ca2+ (50)
a. Average of five analyses of each samples ± standard deviation (n = 5)
Chromium is masked using methyl isobutyl ketone.
116
TABLE 4C2 DETERMINATION OF VANADIUM IN SOME SYNTHETIC MIXTURES USING
SAFRANINE O AS A REAGENT
5��#�� � � � � � � � � 3���%�����%� ��� ��!� �� )����-1) *����� �)*'� )����-1)Recovery Added Founda ±SD (% )
1 Zn2+ (25)+Cd2+ (25) 1.00 0.98±0.02 98.0
2 Zn2+ (25)+Cd2+ (25)+CrVI (5)+Mn2+ (20) 0.50 0.48±0.04 96.0
3. Zn2+ (25)+Cd2+ (25)+CrVI (5)+Mn2+ (20) 0.50 0.50±0.08 100.0
+Ca2+ (50)
a. Average of five analyses of each samples ± standard deviation (n = 5)
Chromium is masked using methyl isobutyl ketone.
TABLE 4C3
DETERMINATION OF VANADIUM IN SOME SYNTHETIC MIXTURES USING
LEUCO XYLENE CYANOL FF AS A REAGENT
5��#�� � � � � � � � � 3���%�����%� ��� ��!� �� )����-1) *����� �)*'� )����-1)Recovery
Added Founda ±SD (% )
1 Zn2+ (25)+Cd2+ (25) 1.00 1.02±0.03 102.0
2 Zn2+ (25)+Cd2+ (25)+CrVI (5)+Mn2+ (20) 0.50 0.48±0.06 96.0
3. Zn2+ (25)+Cd2+ (25)+CrVI (5)+Mn2+ (20) 0.50 0.47±0.12 94.0
+Ca2+ (50)
a. Average of five analyses of each samples ± standard deviation (n = 5),
Chromium is masked using methyl isobutyl ketone.
117
TABLE 4D1DETERMINATION OF VANADIUM IN PHARMACEUTICAL SAMPLE USING
TOUIDINE BLUE, SAFRANINE O AND LEUCO XYLENE CYANOL FF AS
REAGENTS
Reagent Samples V V Recovery used Added found a (%)
�����������������)����-1'������)����-1) ± SD Toluidine Blue b Neogadine Elixir® -- 1.82 ± 0.02 98.91
(10mL/100mL) 4.0 5.81 ± 0.04 99.75
6.0 7.78 ± 0.05 99.33
Safranine O b Neogadine Elixir® -- 1.80 ± 0.02 97.8
(10mL/100mL) 5.0 6.82 ± 0.06 99.7
10.0 11.77 ± 0.04 99.4
Leuco Xylene Cyanol FF b Neogadine Elixir® -- 1.81 ± 0.05 98.3
(10mL/100mL) 3.0 4.83 ± 0.03 99.8
6.0 7.74 ± 0.07 98.7
a. Mean ± standard deviation (n = 5)
b. Raptakos Brett & Co. Ltd. Mumbai 400 030, India. [Each 10 mL contains iodised
peptone-0.64 mg, magnesium chloride-13.34 mg, manganese sulphate-2.66 mg,
sodium metavanadate-0.44 mg, zinc sulphate-21.42 mg, pyridoxine HCl-0.50 mg,
cyanocobalamin-0.33 mg, nicotinamide-6.66 mg, alcohol(95 %)-0.63 mL, total
alcohol 6 %(v/v)], vanadium taken-1.84 ����-1.
118
TABLE 4D2 COMPARISON OF THE METHOD REPORTED WITH EARLIER METHODS
ε = Molar absorptivity, ss = Sandell’s sensitivity
Reagent Method Beer’s law)����-1)
ε (Lmol-1cm-1)%%�)��$�-2)
λmax(nm)
Ref. No.
Arsenazo-M Spectrophotometry 0-������ ε = 1.04×103
-----547 81
DABH Spectrophotometry 0-1.5 ε = 2.83×104 ---- 83Thionin Spectrophotometry 0.2-10 ε = 2.298×104
ss = 0.520×10-2600 85
Variamine blue Spectrophotometry 0.1-2.0 ε = 1.65×104
ss = 3.0×10–3570 86
Rhodamine-B Spectrophotometry 0.08-0.64 ε = 1.3×105
ss = 9.0×10–4553 88
Proposed MethodToluidine blue
Safranine O
Leuco xylene cyanol FF
Spectrophotometry
Spectrophotometry
Spectrophotometry
0.4–8.0
0.5–12.4
0.05–8.0
ε = 2.141×104
ss = 2.36×10-3
ε = 3.06×104
ss = 1.66×10-3
ε = 1.16×104
ss = 4.38×10-3
628
530
614
119
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