Upload
lykhanh
View
219
Download
1
Embed Size (px)
Citation preview
27 International Journal of Analytical and Bioanalytical Chemistry 2013; 3(1): 27-35
ISSN-2231-5012
Original Article
Extractive separation of Vanadium(V) from succinate medium by solvent
extraction using 2-n-octylaminopyridine
Leena E. Noronhaa,b
, Ganesh S. Kamble a,c
, Sanjay S. Kolekara, Mansing A. Anuse*
a Analytical Chemistry Laboratory, Department of Chemistry, Shivaji University, Kolhapur, 416 004, India
b Department of Chemistry, Vivekanand College Kolhapur, India
c Department of Engineering Chemistry, KIT’s College of Engineering, Kolhapur, India
Received 01 February 2013; accepted 14 February 2013
Abstract
A systematic study of liquid liquid extractive separation of Vanadium (V) was carried out from 25ml 0.01M sodium
succinate solution using 10mL 0.087M 2-n-octylaminopyridine as an extractant. Quantitative extraction of Vanadium
(V) was observed at pH 3.0-5.0 in the range of 0.005-0.02M sodium succinate with 0.087M 2-n-OAP in xylene.
Vanadium(V) was back extracted with 6M NH3(3x10mL) and determined spectrophotometrically by 8-quinolinol
method. Various parameters such as effect of acid concentration, stripping agents, equilibration time, loa ding
capacity, aqueous to organic volume ratio, reagent concentration, diluents were studied. From the temperature study
the enthalpy change (∆H) of the extraction was recorded as 34.464KJ mol-1
.The nature of the extracted species in
organic phase was determined by using conventional slope analysis method. The extraction of Vanadium(V) in acidic
range was found to proceed by ion pair mechanism with extracted species being [(RR’NH
+)2 VO(succinate)
2-2 ](org) .The
proposed method was applicable to separate Vanadium(V) from associate metals like Zr(IV), Mo(VI),
W(VI),Re(VII),Co(II),Ni(II),Zn(II), Fe(III) and Pb(II).The method is further extended for the recovery of
Vanadium(V) from various synthetic mixtures, real samples of alloy, pharmaceutical and certain en vironmental
samples.
© 2013 Universal Research Publications. All rights reserved
Keywords: Vanadium (V), liquid liquid extraction, 2-n-octylaminopyridine.
INTRODUCTION Vanadium is widely distributed throughout the earth but
in rather low abundance ranking twenty second among
the elements of the earth’s crust [1,2]. It is always found
in combination with various minerals such as carnotite,
roscoelite, vanadinite, mothramite and patronite, which
are important sources of the metals [3]. Significant
amounts are present in bauxite and carboniferous
materials such as coal, oil shale and tar sand. [1].
Naturally occurring Vanadium consists of two isotopes 50
V (0.24%) and 51
V (99.76%) of which 50
V form is
slightly radioactive and has a half life of more than
3.9x1017
years.[4]. Vanadium is an important trace metal
of bioinorganic importance [5] and is present in most of
the organisms. A substantial amount of vanadium is
released during burning of crude petroleum, coal and
lignite which would then settle on the soil. Some plants
accumulate vanadium up to 80 µg mL-1
, [6] most of
which is accumulated in leaves and roots. Vanadium acts
as a growth –promoting factor and participates in
fixation and accumulation of nitrogen in plants, while
high concentration of vanadium reduces productivity of
the plants [7].Vanadium is an essential element for
normal cell growth [8]. It is beneficial for prevention of
vascular diseases and also has therapeutic potentials for
diabetes with a definite safe dose range because of its
insulin mimic effects. Vanadium complexes can reduce
growth of cancer cells and improves human diabetes
mellitus [9]. The toxicity of Vanadium is dependant on
its oxidation state with Vanadium (V) being more toxic
than Vanadium (IV) [10]). The amount of Vanadium in
blood and urine depends upon intensity and duration of
its exposure. The threshold limit values (TLV) reported
are 0.5mg/cubic meters of air and 0.1mg/cubic meter of
fume. [11]. The amount of Vanadium in excess of TLV
values is reported to cause anemia, cough, emaciation
and irritation of mucous membrane, gastrointestinal
disturbances and bronchopneumonia.[12]. Industrial
exposure to Vanadium has been showed to cause eye and
lung irritation, inhibition of activity to enzyme
Available online at http://www.urpjournals.com
International Journal of Analytical and Bioanalytical Chemistry
Universal Research Publications. All rights reserved
28 International Journal of Analytical and Bioanalytical Chemistry 2013; 3(1): 27-35
cholinesterase.[13]. Industrial applications of Vanadium
include dyeing, ceramics, ink and catalyst manufacture.
Discharges from industries contribute to its presence in
the water supply. [14]. In this country the tolerable level
of Vanadium in drinking water is 100 µgL-1
.The most
important use of Vanadium is as an alloying element in
steel industry where it is added to produce grain
refinement and hardenability in steels. Vanadium steels
are used in dies or tapes because of their depth
hardening characteristics and for cutting tools because of
their wear resistance. They are also used as
constructional steel in both light and heavy sections, for
heavy ions and steel castings, forged parts such as shafts
and turbine motors, automobile parts like gears and axles
and for springs and ball bearings. Vanadium is an
important component of ferrous alloys used in jet
aircraft engines and turbine blades where high
temperature creep resistance is a basic requirement. It is
also used as an additive to titanium alloys for aerospace
applications. [15]
Several high molecular weight amines have been used
for solvent extraction of Vanadium. They are N-p-
octyloxybenzoly-N-phenylhyroxyl amine, [16],
trioctylamine[17], diisododecylamine[18], primene 81R
and alamine 336 [19]and tricapryl methyl ammonium
chloride[20]. Extraction of Vanadium by
organophosphorus compounds like, Tri-n-butyl
phosphate(TBP) [21], TBP and tri-n-octyl phosphine
oxide (TOPO)[22,23], di-(2-ethyl hexyl)-phophoric acid
(D2EHPA)[24,25],D2EHPA/TBP[26] and
D2EHPA/TOA[27] was successfully carried out. The
other extractants employed for liquid liquid extraction of
Vanadium were 2-hydroxy-4-methoxy-5-methyl
chalkone oxime, (HMMCO)[28], aliquat-336[29,30,31],
rotaxane hydroxamic acid[32], 8-quinolinol [33] and
LIX.63[34]
The present paper deals with liquid- liquid extraction of
Vanadium (V) with 2-n-octylamino pyridine which gives
an ion pair complex extractable into xylene. The aim of
this work is to develop an efficient extraction process for
the sequential separation of V (V) and Mo (VI).The
method is further applied for the separation of V (V)
from commonly associated metals and for analysis of
several samples with good results.
Experimental Apparatus
An Elico digital pH meter model LT – 120 was used for
pH measurement. Labtronics UV-VIS digital
spectrophotometer model LT-29 with 1 cm quartz cells
was used for absorbance measurements. Tapson’s
analytical single pan balance model 200 T having 0.001
gm accuracy was used for weighing.
Doubly distilled water and analytical reagent – grade
chemicals (BDH or Merck) were used throughout this
study. All apparatus were used during the time period
from January to May 2012.
Reagents
Standard Vanadium (V) solution.
A stock solution of Vanadium (V) was prepared by
dissolving previously ignited Vanadium pentoxide in dil.
NaOH which was acidified with sufficient amount of
conc.H2SO4 and then diluted to 1000ml with doubly
distilled water. The solution was standardized by known
method.
A working solution of 10 µg/mL was made by
appropriate dilution.
2-n-Octylaminopyridine was synthesized by Borshch and
Petrukhin method [35] and its solution was prepared in
xylene (S.D. fine).
0.5 percent 8- quinolinol was prepared in chloroform.
General procedure for the extraction and determination
of vanadium(v))
An aliquot of Vanadium(V) solution containing 50 µg
was mixed with a sufficient quantity of sodium
succinate(0.0675 g) to make its concentration of 0.01 M
in a total volume of 25 mL of the solution.The PH
of the
aqueous solution was adjusted to 3.2 with dilute
hydrochloric acid and sodium hydroxide solution. The
solution was then transferred to a 125 mL separatory
funnel and shaken for 3min. with 10 mL of 0.087M of 2-
n-octylaminopyridine in xylene. The organic phase was
separated and equilibrated with three 10 mL portions of
6M ammonia solution to back extract Vanadium(V). The
back extractants were combined and shaken with 5 mL
of xylene to remove the traces of dissolved amine and
evaporated to moist dryness. Vanadium(V) was
determined spectrophotometrically [40] as follows
The PH
of the aqueous phase was adjusted to 5.0 after
diluting to 25 mL with distilled water. The solution was
then extracted with 2 successive 5ml portions of 0.5%
8quinolinol in chloroform. The black
hydroxyquinolinate complex absorbed at 400 nm. The
amount of Vanadium (V) was computed from a
calibration curve.
Fig.1. Extraction of V (V) as a function of 2-n-
octylaminopyridine concentration
29 International Journal of Analytical and Bioanalytical Chemistry 2013; 3(1): 27-35
Result and discussion Extraction as a function of p
H
The effect of pH
on percentage extraction of Vanadium
(V) was studied with varying pH
range of 1-10 in
presence of weak organic acid such as sodium succinate
(0.01M) with 2-n-OAP in xylene. The extraction of
Vanadium (V) was found to be quantitative in the pH
range 3.0 to 5.0 to form ion pair complex with 0.01M
sodium succinate. An optimum pH 3.2 was used for
efficient extraction of Vanadium (V) for further
recommended procedure.
Extraction of Vanadium as a function of 2-n-
Octylaminopyridine Concentration
In order to optimize for the extraction of Vanadium (V),
xylene solutions of 2-n-octylaminopyridine of varying
concentrations (0.0024-0.49 M) were employed keeping
others parameters like pH, equilibrium time, diluents and
temperature constant. It was found that quantitative
extraction of 50 µg Vanadium (V) from 0.048-0.145 M
2-n-OAP was carried out with 0.01M sodium succinate
at pH 3.2. However increase in the concentration
decreases the extraction. This is due to the formation of
stable ion-pair between 2-n-OAP and succinate.(Fig.1).
Further extraction study of Vanadium (V) was carried
out using 0.087M 2-n-OAP in xylene.
Extraction as a function of weak organic acid
concentration.
The extraction of Vanadium(V) was carried out in
presence of varying concentration of weak acid such as
sodium succinate, sodium malonate, sodium citrate
,sodium tartarate and L-ascorbic acid by keeping all the
parameters constant . The extraction of Vanadium (V)
was found to be quantitative in the range 0.005-0.02M
for sodium succinate, sodium malonate, sodium citrate
and sodium tartarate. There was incomplete extraction of
Vanadium (V) in presence of L-ascorbic acid. However
0.01M sodium succinate was used throughout the
experimental work. [Fig.2]
Fig. 2. Extraction of V (V) as a function of weak
organic acid conc.
Extraction with various diluents
Benzene, xylene, toluene, chloroform, carbon
tetrachloride, amyl alcohol, methyl isobutyl ketone, n-
butanol, kerosene, amyl-acetate and 1, 2 dichoroethane
were examined for use as diluents in the extraction of
Vanadium (V) with 2-n-octylaminopyridine. The most
efficient diluent was found to be xylene.
Effect of stripping agents
Vanadium (V) was stripped with three 10 mL portions of
various stripping agents at different concentrations. The
stripping was found to be incomplete in water(65.31%),
NaOH ( 81.0%), Na2CO3(79.84%),acetic acid(98.45%),
acetate buffer at pH 4.45 (97.25%) and ammonium
chloride-ammonium hydroxide buffer at pH 10.0(7.2%).
But complete stripping was possible using ammonia
(6.0-8.0 M), and KOH (0.5-0.9 M). In the proposed
method 6M ammonia was used as strippant because
it was easier to remove from aqueous phase by
evaporation prior to determining Vanadium (V)
spectrophotometrically. [Table 1].
Effect of equilibration time
When the two immiscible phases were equilibrated for a
period of (0.25 min to 30 min), the extraction was
quantitative over a period of 2-5 min. For the proposed
method, 3 min equilibration time was recommended in
order to ensure complete extraction of Vanadium (V).
Loading capacity of 2-n- OAP
The concentration of Vanadium (V) was varied from 10-
500 µg / 10 mL to determine the loading capacity of 2-n-
octylaminopyridine in xylene. It was found that the
maximum loading capacity of 10 mL 0.087 M 2-n-
octylaminopyridine in xylene was 100µg Vanadium (V).
Effect of aqueous to organic volume ratio
Vanadium (V) was extracted in different aqueous to
organic volume ratios in the range 10-200mL of 0.01m
aqueous sodium succinate medium with 10mL 0.087M
2-n-OAP in xylene. There was sharp increase in the
separation efficiency and distribution ratio of Vanadium
(V) when phase ratio A/O varied from 1:1 to 4:1.
However in the recommended procedure the phase ratio
used was 2.5:1.
Fig. 3.Log-log plot of log D V (V) Vs log C [2-OAP] at
fixed succinate conc
30 International Journal of Analytical and Bioanalytical Chemistry 2013; 3(1): 27-35
Fig. 4. Log-log plot of log D V(V) Vs log C [succinate]
at fixed 2-n-octylaminopyridine conc .
Fig. 5. Effect of temperature on extraction of V (V)
Nature of the extracted species
The probable composition of the extracted species were
ascertained by plotting a graph of log D V (V) against log
C (2-n-OAP) at fixed sodium succinate concentrations (0.01
M) (fig 3). The plots were linear having slopes of 1.8.
and 2.0 at pH 5.0 and 5.5. This indicates that the metal :
extractant ratio was 1:2 Also plots of log D V (V) against
log C (succinate) at fixed 2-n-OAP concentration (0.087 M)
were linear and with slopes of 2.0 and 1.9 (fig. 4). This
indicates two succinate ions participate in the formation
of anionic species. Thus the probable composition of
extracted species is calculated to be 1:2:1(metal:
acid:extractant). A mechanism of the extractant species:
Reaction
RR’NH(org) + H
+(aq) RR
’NH
+2(org) (1)
VO2+
(aq) +2 succinate 2-
VO(succinate)22-
(aq) (2)
2RR’NH
+2(org)+VO(succinate)2
2-(aq)[(RR
’NH2)2
VO(succinate2-
)2 ](org) (3 )
Effect of temperature
The extraction of Vanadium (V) from the aqueous
solution in presence of 0.01 M with 0.087 M of 2-n-
octylaminopyridine in xylene was studied at varying
temperature between 299 and 307 K. The change of
extraction equilibrium constant (kex) with temperature is
expressed by Vant Hoff equation:-
𝑑(𝑙𝑜𝑔 𝑘𝑒𝑥 )
d (
1
T) =
−Δ𝐻
2.303R
The plot of log (kex) Vs 1000/T is linear with slope (-
1.8) and enthalpy change of the extraction reaction was
evaluated as ∆H = 34.464 KJ mol-1
which suggest that
the reaction is endothermic.
The free energy (∆G) and entropy (∆S) were calculated
from eqns (1) and (2). The values of ∆G are negative
while the value of enthalpy is positive. [Table 2]
∆G = 2.303 RT. log kex ………. (1)
ΔS =ΔH−ΔG
T ………. (2)
The negative value of ∆G indicates the reaction is
spontaneous. The positive enthalpy value indicates that
the extraction of Vanadium (V) with 2-n-
octylaminopyridine is favourable with rise in
temperature (Fig. 5).
Effect of diverse ions
The effect of various cations and anions on the recovery
of Vanadium (V) was investigated. The tolerance limit
was set as the amount of foreign ions causing a change
±2% error in the recovery of Vanadium(V). Initially the
foreign ions were added to Vanadium (V) solution in
large excess, 100 mg for anions and 25 mg for cations.
The result shows that most common ions do not interfere
with the determination, suggesting high selectivity of
proposed method. Only some cations such as Al(III),
Ga(III), Fe(III), Nb(V), Ni(II), Tl(I) and Sb(III) can be
eliminated by masking with 10mg F,- 50mg SCN
- and
10mg citrate. The selectivity of this method is
increasesed by using suitable masking agents (Table 2).
The anions such as EDTA and Ascorbate interfered in
the extraction of Vanadium (V) by the proposed method.
Applications
Separation and determination of Vanadium (V) from
binary mixture:
The suitability of above developed method
was examined by applying it to the separation and
31 International Journal of Analytical and Bioanalytical Chemistry 2013; 3(1): 27-35
Table 1: Extraction behaviour of V(V) as a function of stripping agents
% RECOVERY
Molarity NH3 NaOH KOH Na2CO3 CH3COOH
0.1 25.23 49.22 72.20 22.43 50.56
0.2 38.29 52.41 79.87 35.39 55.24
0.3 49.26 61.39 86.90 46.27 60.32
0.4 58.42 72.44 96.42 52.46 69.48
0.5 67.28 75.06 100 55.25 75.74
0.6 70.11 77.24 100 63.29 80.91
0.7 72.24 79.51 100 69.80 85.48
0.9 73.91 81.22 100 74.52 89.92
1.0 74.52 76.24 98.00 76.19 94.28
2.0 87.26 73.59 92.05 79.84 95.08
3.0 90.41 65.04 88.15 66.79 96.14
4.0 93.20 61.16 84.00 61.25 97.21
5.0 96.43 54.12 76.28 59.46 98.45
6.0 100 45.27 65.45 55.24 95.21
7.0 100 - - 50.55 91.16
8.0 100 - - 42.91 88.46
9.0 99.42 - - 37.62 84.23
10.0 95.52 - - 29.28 80.14
Water-recovery 65.31%); Ammonia Buffer (pH=10.0) (7.2%) recovery; Acetate buffer (pH=4.45): recovery 97.25%
Table 2: Effect of diverse ions
Foreign ion Tolerance limit(mg) Masking agent Foreign ion Tolerance limit(mg) Masking agent
Without
masking
agent
With
masking
agent
Without
masking
agent
With
masking
agent
Sr(II) 5 25 10mg citrate Ni(II) 0.5 3 50mg SCN-
Zn(II) 4 20 10mg citrate Al(III) 0.5 2 10mgF-
Ca(II) 4 20 10mg citrate Ga(III) 0.5 5 10mgF-
Mg(II) 4 20 10mg citrate In(III) 0.5 5 10mgF-
Fe(III) 3 25 10mgF- Nb(V) 0.1 1 10mgF
-
Co(II) 2 20 50mg SCN- Tl(I) 0.4 2 10mg citrate
Cd(II) 1.0 15 50mg SCN- W(VI) 0.5 3 10mgF
-
Cr(VI) 1.0 10 10mg citrate Sb(III) 0.5 3 10mg citrate
Au (III) 1.0 10 100mg Br- Acetate 100
Bi(III) 1.0 10 10mg citrate Iodide 100
Pb(II) 1.0 20 100mg I- Bromide 100
Ge(IV) 1.0 10 10mgF- Thiourea 100
Hg(II) 1.0 20 100mg I- Tartarate 100
Cu(II) 1.0 25 100mg I- Thiocyanate 50
Se(IV) 1.0 15 10mg citrate Nitrate 50
Ce(IV) 1.0 15 10mgF- Nitrite 50
La(III) 1.0 10 10mgF- Salicylate 50
U(VI) 1.0 10 10mgF- Citrate 10
Th(IV) 1.0 10 10mgF- Fluoride 10
Re(VII) 1.0 10 50mg SCN- Thiosulphat
e 5
Ba(II) 1.0 10 10mg citrate Sulphate 1
Zr(IV) 1.0 5.0 10mgF- Phosphate 1
Mo(VI) 1.0 5.0 50mg SCN- Oxalate 1
determination of Vanadium (V) in varieties of binary
mixtures which are commonly associated with it by
taking the advantages of the difference in extraction
condition of the metal, such as PH of the aqueous phase,
reagent concentration and use of masking agent.
Sequential separation of Vanadium (V) and Molybdenum
(VI): To an aliquot containing 50 µg Vanadium(V) and
400 µg Molybdenum (VI) in a 25 ml volumetric flask
enough sodium succinate and water were added to give a
final concentration of 0.01M. The pH of the solution was
32 International Journal of Analytical and Bioanalytical Chemistry 2013; 3(1): 27-35
Table 3: Separation of V(V) from binary mixtures
Metal ion Amount (µg) Average (%)Recovery Chromogenic ligand Reference No.
V(V)) 40 99.9 8- quinolinol 40
Zr(IV) 100 99.7 Alizarin red S 38
V(V) 40 99.8
Mo(VI) 400 99.6 Thiocyanate 37
V(V) 40 99.8
WVI) a 200 99.8 Thiocyanate 37
V(V) 40 99.9
Ni(II) b
200 99.9 DMG 38
V(V) 40 99.9
Re(VII) 200 99.7 Thiocyanate 37
V(V) 40 99.8
Pb(II) 400 99.5 EBT 39
V(V) 40 99.8
Co(II) 400 99.6 Thiocyanate 38
V(V) 40 99.9
Fe(III) 500 99.8 Thiocyanate 38
V(V) 40 99.9
Zn(II) 500 99.8 EBT 36
V(V) 40 99.9
Cr(VI) 200 99.7 Diphenyl carbazide 38
a masked by 10 mg F-
b masked by 50 mg SCN-
Table 4: Separation of V(V) from synthetic mixtures
Composition (g) Average
Recovery* %
Relative
error
V(V),50;Zr(IV),400; Pb(II), 500 99.9 0.1
V(V),50; Mo(VI), 300; Fe(III),
300 99.8 0.2
V(V),50; Cu(II), 400; Mo(VI),
300 99.9 0.1
V(V),50 ; Bi(III), 400; Au
(III),500 99.8 0.2
V(V),50 ; Hg(II), 500; Sr(II),
500 99.8 0.2
V(V),50; Zn(II), 500; W(VI) a,
300 99.8 0.2
V(V),50 ; Cr(VI), 300; Ni(II) b,
200 99.8 0.2
V(V), 50 ; Re(VII), 300; Th(IV),
400 99.9 0.1
V(V), 50 ;Sb(III)400 c ; Co(II),
300 99.8 0.2
* Average of five determinations; a Masked by 10 mg F-; b
Masked by50 mg SCN-; c Masked by 10 mg citrate
adjusted to 3.2 and this solution was equilibrated with
10mL of 0.087M 2-n-OAP in xylene. Under this
condition Vanadium (V) was quantitatively extracted
into organic phase leaving behind Mo (VI) in the
aqueous phase. The organic phase was back stripped
with (3x10mL) portion of 6M NH3 and Vanadium (V)
was determined spectrophotometrically as recommended
in the procedure. The aqueous phase was reduced and
then mixed with HCL and LiCl to give final
concentration of 2M and 5M respectively in total volume
of 10mL. The solution was than transferred to a 125
separating funnel and shaken for 1 minute with10 mL of
0.233M of 2-n-OAP in xylene. The organic phase was
separated and equilibrated with (3x10mL) of 1M NH3 to
back extracted Mo (VI) which was later determined
spectrophotomerically by thiocyanate method [37]
Vanadium is present with cations such as Fe(III),
Ni(II), Cu(II), Co(II) , Pb(II), Zn(II) and Cr(VI) in
various minerals such as bravite, davidite, roscoelite and
magnetite. Hence it is essential to separate Vanadium
from such cations. Vanadium(V) was separated from
Fe(III), Pb(II) , Zn(II),Re(VII),Cr(VI)andCo(II) by
extraction with 10mL of 0.087M of 2-n-OAP in xylene
from 0.01M sodium succinate adjusting the pH to3.2.
Under these conditions, the added metal ions remained
quantitatively in the aqueous phase. The aqueous phase
was washed with 5mL xylene to remove the traces of the
reagent. Metal ions Pb(II)and Zn(II), from the aqueous
phase were determined complexometrically [36] while
other cations Fe(III), Re(VII), Cr(VI) and Co(II)were
determined spectrophotometrically by standard
methods[Table 3]. Vanadium (V) was determined by the
proposed method after back stripping the organic phase.
Separation of W (VI) and Ni(II) from Vanadium(V) was
carried out by masking them with 10 mg F- and 50mg
SCN- respectively. The masked cations W (VI) and Ni
(II) remained in the aqueous phase under an optimum
condition of Vanadium (V). From the organic phase
Vanadium (V) was stripped with 6M NH3 (3x10 mL) and
determined spectrophotometrically as per general
procedure. After demasking W (VI) and Ni (II) with
5mL HCL acid, the aqueous phase was evaporated to
moist dryness. W (VI) and Ni(II) were determined
spectrophotometrically by Thiocyanate and DMG
respectively
There is co-extraction of Zirconium(IV) under an
optimum condition of Vanadium(V). This was made
possible by selective stripping. Vanadium (V) from the
organic phase was stripped first with 6M NH3 (3x10 mL)
followed by stripping of Zirconium (IV) with 0.5M
HNO3 (3x10 mL). Vanadium (V) was determined by
33 International Journal of Analytical and Bioanalytical Chemistry 2013; 3(1): 27-35
Table 5: Determination of V(V) in alloys
Alloy Sample Composition % Amount
Recovery % V taken % V found %
NBS steel 72
0.301C, 0.54 Mn, 0.014 P, 0.024 S, 0.256 Si,
0.062 Cu
0.05 Ni, 0.89 Cr, 0.005 V, 0.009 N, 0.184 Mo
0.005 0.005 100
NBS STD
sample153a steel
0.90C, 0.192Mn, 1.76W a, 0.023P, 0.007S,
0.27Si, 0.094 Cu, 2.06 V,8.47 Co, 0.024 N,
8.85 Mo
2.06 2.06 100
Tool steel
SRM 134
0.81C, 0.218 Mn, 0.18 P, 0.007 S, 0.323 Si,
0.101 Cu, 0.088 Ni, 3.67 Cr, 1.25 V, 2.0 W a,
8.35Mo
1.25 1.24 99.9
BCS-401
(Low alloy steel)
1.06 C, 0.59 Si, 0.02 Ni, 0.009 S, 0.042 P,
1.0 Mn, 0.1Cu, 0.52 V, 0.52 Mo. 0.52 0.52 100
BCS – 320
Carbon Steel
0.25 C, 0.172 Ni b, 0.37 Si, 0.008 V, 0.024
Sn, 0.02 P, 0.018 Ti, 0.22 Cr, 0.29 Mn, 0.058
As, 0.004 Sb, 0.009 S, 0.25 W, 0.1 Mo
0.008 0.008 100
* Average of five determinations; a Masked by10mg F- ; b Masked by 50 mg SCN-;
Table 6 : Recovery of V (V) from synthetic leach solutions of spent catalyst
Spent catalyst mixtures Composition % Mo(VI) found % Recovery* R.S.D. %
Sample 1 a
10Ala, 3.0Mo, 0.5 V, 0.5Ni
, 1.0
Co, 0.2 Fe 0.5 0.5 100
Sample 2
0.28 Mo, 0.997 Al,
0.091V,0.047Ni,0.095
Co,0.024Fe
0.091 0.091 100
Sample 3a
2.05 Mo, 0.42 V, 5.6 Al, 10.7
SiO2 0.42 0.42 100
* Average of three determinations, a masked by 10 mg F-;
Table 7 : Analysis of V(V) in pharmaceutical drugs
Allopathic
Sample Composition (mg)
Certified
value of
V(V))
mg/tablet
Amount of V(V) found
mg/tablet Recovery* % R.S.D.%
Proposed
method
AAS
method
Maxi Prenatal
support
multivitamin
800mgCa,18mgFe,404mgP, 0.225mg
I,400mg Mg, 15mg Zn, 0.025mg Se,
1mg Cu, 7mg Mn, 0.12 mg Cr, 99
mgK, 1 mgV
1.0 1.0 1.0 100 0.0
Green Pro96
multivitamin)
50 mg Ca, 19 mg P, 225mcg I, 50
Mg,2.0 mg Zn, 0.025mg Se, 0.2 mg
Cu,2mg Mn,
0.05mgCr,0.025mgMo,0.025 mg V
.
0.025 0.025 0.025 100 0.0
Supractiv Abbott
(Piramal
Healthcare Pvt.
Ltd. Chembur,
Munmbai)
10 mg K, 9.07 mg Zn, 5.0 mg Mg, 5.0
mg P, 5.0 mg Ca, 3.86 mg Cu, 2.2
mgMn, 2.0 mg Si, 1.0 mg B0.080 mg
Cr, 0.070 mg Se, 0.050 mg Ni,
0.005mg V, 0.002 mgSn, 0.5 mg Mo
0.005 0.005 0.005 100 0.0
*Average of five determinations.
recommended procedure while Zirconium (IV) was
determined by Alizarin Red S spectrophotometrically.
Determination of Vanadium (V) in synthetic mixture
The applicability of the developed method for the
separation and determination of Vanadium (V) in
synthetic mixtures was studied [Table 4]. In the
synthetic mixtures, Vanadium was extracted under the
optimum extraction conditions and quantitatively
recovered in all the mixtures.
Determination of Vanadium (V) from alloys
(NBS steel 72, NBS STD 153a steel, Tool steel SRM
134a, BCS-401and BCS-320)
About 0.05 g of each sample of alloy was dissolved in
10 mL of aqua regia and heated to moist dryness.
Further 5 mL conc. hydrochloric acid was added to the
mixture and heated to expel the nitrate. The residue
obtained was filtered through Whatmann filter paper
No.1 to remove silica and metastannic acid if present.
34 International Journal of Analytical and Bioanalytical Chemistry 2013; 3(1): 27-35
Table 8: Determination of vanadium content in environmental samples
Samples Vanadium added
(g)/mL
Vanadium
found(g)/mL Recovery %
SOIL
A
B
25.0
35.0
25.0
35.0
100
100
NATURAL WATER
C
D
10.0
15.0
10.0
15.0
100
100
SEA WATER
E
F
5.8
9.5
5.8
9.5
100
100
PLANT MATERIAL
Tobacco
Carrots
Almonds
Tea leaves
Rice
16.5
15.3
30
6.5
5.4
16.2
15.0
30
6.5
5.4
100
98.03
100
100
100
The filtrate obtained was diluted to 50 mL with distilled
water. An aliquot from each alloy solution was then
analysed by the proposed method to determine
Vanadium (V) [Table 5].
Determination of Vanadium (V)) from environmental
samples A] SOIL:
An air dried homogenized soil sample (1g) was weighed
accurately and placed in a 100 mL kjeldahl flask. The
sample was digested in presence of 50mL concentrated
HCL and 10mL of concentrated HNO3 for 1 hr. on a
sand bath. The solution was then evaporated to dryness.
The residue was boiled with 50mL of 0.1M HCL acid
and filtered. The filtrate and washings were evaporated
to dryness and the residue was taken up and the solution
diluted accurately to 100mL with 0.1M HCL acid. An
appropriate aliquot was used for the analysis of
Vanadium (V) by the proposed method.
B] WATER:
The required amount of water samples were filtered and
analyzed for vanadium. They tested negative. To these
samples, known amount of vanadium (V) were added
and analyzed by the proposed procedure for vanadium.
C] PLANT MATERIAL
To 10g food samples 25mL concentrated HCL was
added, followed by digestion on a sand bath for 1 hour
and evaporation to dryness. The residue was dissolved in
10-15mL concentration HCL along with 0.5g ammonium
persulphate and digested for 20 min on a sand bath.
Later the contents were boiled with 20mL of 0.1m HCL
and finally the filtrate and washings were diluted to 100
mL with doubly distilled water.
An appropriate aliquot was used for the analysis by the
proposed method. Whenever the measured signal
exceeded that of a linear working range the sample was
further diluted.
Recovery of Vanadium (V) from synthetic leach solutions
of spent catalyst
The synthetic leach solutions of spent catalyst were
masked by 50 mg thiocyanate and extracted with 10 mL
of 0.087 M 2-n-octylaminopyridine in xylene in
presence of 0.01M sodium succinate. The aqueous phase
was first separated for removal of Al, Mo, Ni, Co, Fe
and SiO2.The organic phase containing Vanadium (V)
was then stripped with 6M ammonia (3x10mL) and then
washed with 5 mL xylene to remove the traces of amine
and used to determine Vanadium (V) by the proposed
method [Table.9].
Analysis of Vanadium (V) in pharmaceutical drugs
Pharmaceutical allopathic tablets such as Supractive,
MaxiPrenatal Support and Green Pro 96 multivitamins
were selected for the analysis of Vanadium(V).A known
weight of the sample was dissolved in 5.0 mL of aqua
regia solution and evaporated to moist dryness by
heating gently on a hot plate. Addition of perchloric acid
was avoided to stop spurting. The residue obtained was
dissolved in 1:1 HCL and filtered through Whatmann
filter paper No.1. The filtrate was diluted to 100 mL in a
standard volumetric flask with distilled water. An
aliquot of each solution was then taken for the extraction
of Vanadium (V) by the proposed method. The results
obtained were confirmed by AAS (Table.10).
Conclusions The important features of the method described here are:
Quantitative extraction of Vanadium (V) was achieved
in 3 min. with 0.087 M of 2-n-octylaminopyridine in
xylene. Very low reagent concentration is required for
the extraction. The extraction mechanism corresponds to
form an ion pair complex of [(RR’NH2)2 VO (succinate
2-)2
](org) in the organic phase. The method is free from the
interferences of large number of foreign ions. The
proposed method is simple, rapid, selective, reproducible
and suitable for separation and determination of
Vanadium (V) from associated metal ions, synthetic
mixtures, alloys, pharmaceutical samples, synthetic
leach solutions of catalyst and various environmental
samples.
35 International Journal of Analytical and Bioanalytical Chemistry 2013; 3(1): 27-35
Acknowledgements
The authors are grateful to UGC – SAP and DST – FIST
for providing financial assistance. The author expresses
her gratitude to Secretary, Vivekanand Shiksan
Sanstha’s, Mrs. Shubhangi Gavade for her kind
encouragement.
REFERENCES
1. Moskalyk; R.R., Alfantazi, A.M., 2003, processing of
vanadium: a review, Minerals Engineering 16, 793-
805.
2. Hanashi, F., 2002. Two hundred years of vanadium
conference of Metallurgists, Monteal, Canada, August
11-14, 3-15.
3. Perron, L.2001, vanadium, Natural Resources Canada,
Minerals and sector, Canada, Minerals yearbook, pp
59.1-59.7
4. Bauer, G. Guther, V., Hess, H., Otto, A., Roidi, O.,
Roller, H., Sattelberger, S., 2002. Vanadium and
vanadium compounds, Willey- VCH verlag
GmbH,Weinheim, Germany.
5. Nielsen F H and uthus E O, The Essential and
Metabolism of vanadium, Vanadium in Biological
systems, Phsiology and Biochemistry, edited by N. D
Chasteren, (Kluwer Accudemic publishers , The
Netherlands) 1990.
6. Panichev N. Mandiwana K. Moema D. Molthegi R R
and Ngobeni P, J Hazard Mat, A 137 (2006) 649.
7. Taylor M J C and Vanstaden J F, Analyst, 119 (1994)
1263.
8. Narayana , S.L, Reddy, Reddy, S.A.N., Sarala, Y., and
Reddy, A.V. (2008). EnvironmentalMonitoring and
Assessment, (2008) 144, 341-349.
9. Wei, J., Teshima , N., and Sakai T. (2008), Analytical
Sciences,24, 371-376 10.Patel B, Hendersen G.E
Haswell S.J and Grzeskowiak R, Analyst 115 (1990),
1063.
10. Murty KVS, Devi R R and Naidu G R K, Chem
Environ Res. 3 (1994) 129.
11. Casserly D, TLV- CS Committee, university of
Houston at clear Lake, Houston, (2006).
12. Bertini I, Gray H B, Lippard S J and valentine J S,
Bioinorganic chemistry (viva Books private Limited,
New Delhi) 1998.
13. APHA, standard Methods for the Examination of water
and wastewater, 19th
Edn, (American Public Health
Association, Washington DC) 1995, pp.3101.
14. Vanadium and vanadium alloys, in ECT first ed.,
vol.14, p.583 by JeromeStrauss, Vanadium corp. of
America.
15. S.Inoue, T. Hisamori,S. Hoshi and M. Matsubara,
Talanta,1989,36.no.7,794-797.
16. A.Chagnes,M.N.Rager,B.Courtaud,J.ThiryandG.Cote,
Hydrometallurgy,2010,104, 20-24.
17. A.A.Palant , V.A. Bryukvin and V.A.Petrova,Russ. J.
of Inorg. Chem, 2007, 52, no.6, 963-968.
18. L. J. Lozano, C. Godinez, Minerals Engineering,
200316, 291-294.
19. T.Sato, S. Ikoma and T. Nakamura,
J.Inorg.Nucl.Chem. 1977, 39,395-399.
20. P.H.Tedesco, V.B. de Rumi, J. Inorg. Nucl. Chem..
1980,42,269-272.
21. T.Sato, S. Ikoma and T. Nakamura, Hydrometallurgy,
1980,6,13-23.
22. T.Sato,J. Inorg. Nucl. Chem., 1979, 41, 1605-1607.
23. J.P. Brunette, F.Rastegar and M.J.F.Leroy,J. inorg.
Nucl. Chem.,1978,41,735-737.
24. T.Sato, T. Nakamura and M.Kawamura,J. Inorg. Nucl.
Chem., 1978,40,853-856.
25. X. Li Chang Wei, Z.D.Mintig Li, C. Li. Gang Fan.
Hydrometallurgy, 2011, 105,359-363.
26. S.Banerjee, S. Lahiri, S, B,Monohar, A. Ramaswami,
Applied radiation and isotopes, 2002, 56, 571-575.
S.B. Gholse and R.B. Kharat, Microchemical journal,
1984, 30, 297-303.
27. Y.Bal, K. E. BAL, G. Cote, MineralsEng. 2002,
15,377-379.
28. Y.A. El. Nadi, N. S. Awwad, A.A.Nayl, Int. J. Miner.
Process, 2009, 90,115-120.
29. N. Shah and M.N.Desai, Talanta, 1991, Vol. 38, no. 6,
649-652.
30. Y. K Agrawal and C.R. Sharma, Indian Journal of
Chem. 2007, 46A; 1772-1777.
31. S Kawakubo, Y Tsuchiya, M. Iwatsuki, Anal. Chem.
Acta, 1995, 310, 501-507.
32. P. Zhang, K Inoue, K Yoshizuka, H Tsuyama,
Hydrometallurgy, 1996, 41,45-53.
33. N.A. Borshch, O.M. Petrukhin, Zh. Anal. Khim. 33,
1805, 1978.
34. A.I. Vogel, A Textbook of Quantitative Inorganic
Analysis, including elementary instrumental analysis,
3rd
edition, ELBS and Longmann, 1975.
35. E.B. Sandell, Colorimetric determination of traces of
metals, 3rd
edition, Interscience Publishers, Inc. New
York, 1965.
36. Z. Marczenko, Spectrophotometric determination of
elements, Ellis Horwood Limited, Chichester, 1976.
37. F.J. Welcher, The Analytical uses of Ethylene
diaminetetraacetic acid, D. Van Nostrand company
Inc. New York, 1958.
38. G.H. Morrison, H. Freisier, Solvent Extraction in
Analytical Chemistry John Wiley and Sons Inc. New
York, 1966.
Source of support: UGC – SAP and DST – FIST; Conflict of interest: None declared