W.N. El-Sayed, J. Alkabli, K. Althumayri et al.
Journal of Molecular Liquids xxx (xxxx) xxx
them the advantage of the ability to chelate diverse metal ions with pH-
controlled selectivity and pH-dependent stability [23].
DMSO‑d
6
) δ (ppm): 161.33, 158.21, 137.86, 136.22, 133.14, 132.42,
125.02, 123.07, 122.70, 118.74, 117.63, 57.62, 55.91, 54.81, 51.970,
49.02, 36.13, 32.97, 31.61, 31.09, 21.34, 19.17 and 13.61. 3 P NMR
1
Amongst toxic heavy metal ions (HMIs) popularly distributed in
aqueous environments, cupric (Cu(II)) and ferric (Fe(III)) ions were
deemed as potential toxicity sources [24,25] due to their capacity to
generate free radicals and reactive oxygen species (ROS) in the live
cells [24,26], inducing their programmed death. The major sources of
the toxic ferric ions in aqueous environments are; steel tempering, min-
ing, coal coking, and metallurgical industries [27].On the other hand, cu-
pric ions have emitted in aqueous effluents as a result of many industrial
processes, such as electroplating, metal finishing, etching, and plastics
1
9
(202 MHz, DMSO‑d
(471 MHz, DMSO‑d ) δ: −70.57 (d, J = 711.2 Hz). ESI-MS: in positive
mode peaks at m/z 568.4 ([C25
6
): δ −142.95 (hept, J = 711.2 Hz). F NMR
6
+
−
H
37
F
6
N
5
OP] , M – PF
) a.m.u. Anal. Calcd. for C25
(M = 713.53 g/mol): C, 42.08; H, 5.23; N, 9.82%. Found: C,
41.99; H, 5.31; N, 9.78%.
6
) a.m.u. and
2
+
−
211.6 ([C25
OP
H
37
N
5
O] , M – 2 PF
6
37 12
H F
N
5
2
2.3. Deprotonation constant (pKa) of ABIIL
[28]. As the Cu(II) and Fe(III) ions are very toxic metal even at low con-
centrations, therefore, the cupric- and ferric-polluted wastewater
should be remediated before discharging into the aquatic environment
The dissociation constant (pK
aqueous solution (10 M) of ionic strength of 0.04 M (KNO ) by titra-
a
) of ABIIL was estimated at 298 K in its
−4
3
[27,28].
−3
tion with an aqueous NaOH solution (1.6 × 10 M).
.4. Scavenging of Cu(II) and Fe(III) ion by ABIIL extractant
A general protocol mimic to the common solid-phase extraction
Few trials have been reported to remove cupric and ferric ions from
aqueous solutions using TSILs. For instants, imidazolium-supported
TSILs have been applied as scavengers for M(II/III) ions (M = Cu, Co,
Ni, Zn, Cd, Fe) from their respective aqueous solutions; by chelating
them [20,29]. In addition, ammonium-based TSILs showed moderate
to good effect in removing and recovering of several metal ions (Cu
2
(
(
SPE) technique [32] has been utilized for removal of heavy metal ions
HMIs) (Cu(II) and Fe(III)) from aqueous ethanolic solutions by ABIIL
(
II), Pb(II), Zn(II), Cd(II), Ni(II), Co(II), and Fe(III)) from aqueous efflu-
as an extracting agent. In brief, a solution of metal ion (0.5 mmol,
.10 g Cu(CH CO ·2H O; 0.302 g Fe(NO ·9H O) in distilled water
5 mL) was slowly added to the pale-yellow solution of ABIIL (0.71 g,
.0 mmol) in ethanol (30 mL) containing 100 μL of 0.1 M NaOHaq
Then, the reaction mixture was heated under reflux with stirring for
h. After cooling to ambient temperature, the isolated colored solids
were collected by filtration, washed with cold ethanol and diethyl
ether, (2 × 3 mL) for each, and dried in a desiccator. Samples of the ob-
tained complexes were analyzed as follow;
ents [29,30]. Recently, microcapsules composed of styrene and
divinylbenzene were used to encapsulate pyridinium TSILs for Zn(II)
and Cu(II) recovery from aqueous media [31]. Nevertheless, these re-
ported TSILs are limited and their routes of fabrication are sophisticated
and expensive.
All these aforementioned facts prompted us to design and fabricate a
new azomethine-supported bis-butylimidazolium chelating task-
specific ionic liquid (ABIIL) which will be utilized not only for the re-
moval of Cu(II) and Fe(III) ions from the aqueous solutions but also to
convert these ions to metals-based pharmacological nominates.
0
(
1
3
)
2 2
2
)
3 3
2
.
1
[
2
Cu(ABIIL) ] (Cu-ABIIL): Dark yelowish green crystals, Yield
−
1
6
1
9%. FTIR (KBr, cm ): 3125 (w, br), 1647 (m, sh), 1622 (s, sh),
549 (s, sh), 1457 (m, sh), 1336 (m, sh), 1271 (m, sh), 1150 (m,
2. Experimental part
sh), 837 (vs, sh), 643 (m, br), 525 (w, br), 478 (m, sh). ESI-MS:
+
in positive mode peaks at m/z 1315.3 ([C48
H
68CuF18
, M – 2 PF
6
N
10
O
2
P
3
]
, M
) a.m.u.,
) a.m.u., and 220.0 ([C48
). Anal. Calcd. for C48 68CuF24
M = 1460.54 g/mol): C, 39.47; H, 4.69; N, 9.59%. Found: C,
2.1. Materials and instrumentation
−
2+
−
-
3
H
PF
6
) a.m.u., 585.2 ([C48
H
68CuF12
N
10
O
2
P
2
]
3
+
−
41.6 ([C48H68CuF N O P] , M – 3PF
68CuN10
6 10 2 6
Chemicals, solvents, and practical procedures utilized in the prepa-
4
+
−
O
2
]
, M – 4 PF
6
H
10 2 4
N O P
ration of salicylaldehyde-supported butylimidazolium ionic liquids
SBIILs) (2a,b) and 1-(3-aminopropyl)-3-butyl-1H-imidazolium
(
(
3
9.42; H, 4.71; N, 9.38%.
3
Fe(ABIIL) (H O)(NO )] (Fe-ABIIL): Dark purple powder, Yield
5%. FTIR (KBr, cm ): 3453 (m, br), 3122 (w, br), 1620 (s, sh),
549 (s, sh), 1458 (m, sh), 1336 (s, sh), 1272 (m, sh), 1151 (m,
hexafluorophosphate (5) coupled with the instrumentation used for
the comprehensive characterization of prepared compounds were de-
scribed in the online electronic supplementary information (ESI†).
[
2
2
−
1
6
1
sh), 839 (vs, sh), 653 (m, br), 506 (w, br), 458 (w, br). ESI-MS:
2
.2. Synthesis of ABIIL
+
in positive mode peaks at m/z 1387.6 ([C48
70
2+
6 3
H F18FeN11O P ] ,
−
−
M – PF
u., 365.7 ([C48
6
) a.m.u., 621.2 ([C48
FeN11
, M – 4 PF
M = 1532.86 g/mol): C, 37.61; H, 4.60; N, 10.05%. Found: C, 37.52;
H
70
F
12FeN11
O
6
P
2
]
, M – 2 PF
) a.m.u., and 238.1
). Anal. Calcd. for C48
6
) a.m.
Into a 100 mL round-bottomed flask (RBF), a solution of SBIIL (2b)
H
70
F
6
O
6 6
P]3 , M – 3 PF
+
−
(
1.62 g, 4 mmol) in ethanol (35 mL) was gradually added to an ethanolic
4
+
−
(
[C48H70FeN11
O
6
]
6
70 6 4
H F24FeN11O P
solution (25 mL) of the aminopropyl derivative (5) (1.31 g, 4 mmol)
containing a catalytic amount of glacial acetic acid (three drops) under
stirring. Then, the reaction mixture was heated under reflux and contin-
uous stirring for 3–5 h (TLC was used to monitor the completion of re-
action). After reaction completion, the solvent was partially
evaporated followed by cooling of the content of RBF to ambient tem-
perature. The precipitated product was filtered, washed with cold etha-
nol and ether, (3 × 5 mL) for each, dried, and then recrystallized from
aqueous ethanol to give ABIIL as yellow fine crystals. Yield (2.49 g,
(
H, 4.63; N, 9.98.
2.5. Regeneration of ABIIL scavenger
An aqueous solution containing a mixture of HCl (1.0 M, 3 mL) and
thiourea (4% w/v) was added to the extracting products (M-ABIIL com-
plexes) (100 mg). Thereafter, these mixtures have subjected to ultra-
sonic irradiation for 30 min. The color change of the reaction solution
from colorless to yellow color was an indication of the progress of the
ABIIL-recovering process. After reaction completion, the reaction mix-
8
2
1
9%), mp 98–99 °C. FTIR (KBr, cm−1): 3336 (m, br), 3079 (m, br),
982 (m, sh), 2959 (m, sh), 2889 (m, sh), 1631 (vs, sh), 1567, 1549,
466 (s, sh), 1335 (m, sh), 1279 (s, sh), 1150 (s, sh), 965(m, sh), 836
1
(
vs, sh), 735 (m, sh). H NMR (200 MHz, DMSO‑d
6
) δ (ppm): 10.19 (s,
3
ture was neutralized with an aqueous NaHCO solution (1.0 M) which
1H), 9.43 (s, 1H), 9.12 (s, 1H), 9.04 (s, 1H), 8.11–7.96 (m, 2H),
7.82–7.76 (m, 2H), 7.39 (d, 1H, J = 7.1 Hz), 7.06–7.01 (m, 2H), 5.69 (s,
2H), 5.10 (t, 2H, J = 6.9 Hz), 4.26 (t, 2H, J = 7.2 Hz), 4.11 (t, 2H, J =
6.9 Hz), 3.99 (t, 2H, J = 6.8 Hz), 2.25–2.09 (m, 6H), 1.96–1.81 (m, 4H),
0
.93 (t, J = 7.2 Hz, 3H), 0.85 (t, J = 7.3 Hz, 3H). 13C NMR (125 MHz,
leads to the precipitation of the parent scavenger (ABIIL). The recovered
ligand (ABIIL) was collected by filtration, washed several times with
Milli-Q water to remove the undesired byproducts (M-thiourea com-
plexes). Then, this scavenger was dried under reduced pressure and
can be used for a further removal process.
2