3752
S. Sayin et al. / Tetrahedron 67 (2011) 3743e3753
p-tert-butylcalix[4]arene derivative, then washed with water and
dried under vacuum.
For this propose, cations were used as corresponded with one
hundred-fold of uranyl cation concentration.
For 6: the IR spectral data is as (KBr disk) cmꢀ1: 3251,1646 (amide
C]O), 1479, 1410 (aromatic C]C), 1191, 1044, 945, 789 (SieO) and
572 (FeeO).
Acknowledgements
For 7: the IR spectral data is as (KBrdisk) cmꢀ1: 3424,1648 (amine
band), 1598, 1408 (aromatic C]C), 1150, 1046, 950, 781 (SieO) and
574 (FeeO).
We would like to thank The Scientific and Technological Re-
search Council of Turkey (TUBITAK Grant No. 107T873) and The
Research Foundation of Selcuk University (BAP) for financial sup-
port of this work.
4.4. Extraction studies
References and notes
4.4.1. Dichromate/arsenate anion extraction studies. The extraction
capacities of the synthesized calixarene derivatives (4e7) were
determined by the following technique.2 An aqueous solution
(10 mL) containing Na2Cr2O7 or Na2HAsO4 solution at a concentra-
1. Agency for Toxic Substances and Disease Registry (ATSDR), Top 20 hazardous
2. Sayin, S.; Ozcan, F.; Yilmaz, M. J. Inclusion Phenom. Macrocyclic Chem. 2010, 67,
385e391.
3. Bayrakcı, M.; Ertul, S¸ ; Yilmaz, M. Tetrahedron 2009, 65, 7963e7968.
4. Sayin, S.; Ozcan, F.; Yilmaz, M. J. Hazard. Mater. 2010, 178, 312e319.
5. Yolcubal, I.; Akyol, N. H. Chemosphere 2008, 73, 1300e1307.
6. Chakraborti, D.; Mukherjee, S. C.; Pati, S.; Sengupta, M. K.; Rahman, M. M.;
Chowdhury, U. K.; Lodh, D.; Chanda, C. R.; Chakraborti, A. K.; Basu, G. K. Environ.
Health Perspect. 2003, 1, 1194e1201.
7. Kartinen, E. O., Jr.; Martin, C. J. Desalination 1995, 103, 79e88.
8. Chen, R.; Zhang, Z.; Feng, C.; Lei, Z.; Li, Y.; Li, M.; Shimizu, K.; Sugiura, N. Appl.
Surf. Sci. 2010, 256, 2961e2967.
9. Brammer, H.; Ravenscroft, P. Environ. Int. 2009, 35, 647e654.
10. Giral, M.; Zagury, G. J.; Deschenes, L.; Blouin, J.-P. Environ. Pollut. 2010, 158,
1890e1898.
11. Bhattacharya, P.; Welch, A. H.; Stollenwerk, K. G.; McLaughlin, M. J.; Bundschuh,
J.; Panaullah, G. Sci. Total Environ. 2007, 379, 109e120.
12. Patel, S.; Mishra, B. K. Tetrahedron 2007, 63, 4367e4406.
13. (a) Barnhart, J. J. Soil Contam. 1997, 6, 561; (b) Kotas, J.; Stasicka, Z. Environ.
Pollut. 2000, 107, 263e283.
tion of 1.0ꢃ10ꢀ4 M and calixarene derivative (10 mL of 1ꢃ10ꢀ3
M
solution of 4 or 5 in CH2Cl2 for liquideliquid extraction, 25 mg of 6
or 7 for solideliquid extraction) were mixed in a stoppered flask
that was shaken at 175 rpm at 25 ꢂC for 1 h. The ligands were
separated before measurements. The residual dichromate concen-
tration was determined spectrophotometrically by UVevis analysis
at 346 nm as described previously.49 The concentration of arsenate
ion remaining in the aqueous phase was determined spectropho-
tometrically at 610 nm as described previously.50 The effect of pH
was studied by adjusting the pH of the aqueous solutions using
diluted HCl and KOH solutions at 25 ꢂC. The experiments were
performed in triplicate.
The percent extraction (E %) was calculated according to Eq. 1;
14. (a) Losi, M. E.; Amrhein, C.; Frankenberger, W. T. Rev. Environ. Contam. Toxicol.
1994, 136, 91e121; (b) Viamajala, S.; Peyton, B. M.; Sani, R. K.; Apel, W. A.;
Petersen, J. N. Biotechnol. Prog. 2004, 20, 87e95.
A0 ꢀ A
ðE%Þ ¼
ꢃ 100
(1)
A0
15. Migianu-Griffoni, E.; Mbemba, C.; Burgada, R.; Lecercle, D.; Taran, F.; Lecouvey,
where A0 and A are the initial and final concentrations of the di-
chromate/arsenate or uranyl ion before and after the extraction,
respectively.
M. Tetrahedron 2009, 65, 1517e1523.
16. Van Horn, J. D.; Huang, H. Coord. Chem. Rev. 2006, 250, 765e775.
17. WHO Guidelines for Drinking Water Quality 3rd ed., Addendum to Vol. 2,
Health criteria and other supporting information WHO/EOS/98.1 Geneva 2003.
18. Murty, B. N.; Jagannath, Y. Y. S.; Yadav, R. B.; Ramamurty, C. K.; Syamsundar, S.
Talanta 1997, 44, 283e295.
4.4.2. Uranyl cation extraction studies. Into a vial was pipetted an
aqueous solution (10 mL) containing UO2(AcO)2$2H2O at a con-
centration of 1.15ꢃ10ꢀ5 M, a few drops of 0.01 M KOH/HCl solution
in order to obtain the desired pH at equilibrium and maintain the
19. Sadeghi, S.; Doosti, S. Sens. Actuators, B 2008, 135, 139e144.
20. Gupta, A. K.; Gupta, M. Biomaterials 2005, 26, 3995e4021.
ꢁ
ꢁ ꢁ
ꢂ
ꢂ
ꢂ
21. Krizova, J.; Spanova, A.; Rittich, B.; Horak, D. J. Chromatogr., A 2005, 1064,
247e253.
22. Ito, A.; Shinkai, M.; Honda, H.; Kobayashi, T. J. Biosci. Bioeng. 2005, 100, 1e11.
23. Mornet, S.; Vasseur, S.; Grasset, F.; Veverka, P.; Goglio, G.; Demourgues, A.;
Portier, J.; Pollert, E.; Duguet, E. Prog. Solid State Chem. 2006, 34, 237e247.
ionic strength, and calix[4]arene derivatives (10 mL of 1ꢃ10ꢀ3
M
solution of 4 or 5 in CH2Cl2 for liquideliquid extraction, 25 mg of 6
or 7 for solideliquid extraction). The mixture was vigorously agi-
tated in a stoppered glass vial with a mechanical shaker for 2 min,
then was shaken at 175 rpm at 25 ꢂC for 1 h. The ligands were
separated before measurements. The residual uranyl concentration
of aqueous solute was determined spectrophotometrically.51
Blank experiments showed that no uranyl extraction occurred in
the absence of calixarene. The uranyl cation in aqueous phase
measured at 652 nm (for pH 5.5e8.5). The percent sorption (E %)
was calculated52 according to the above equation.
€
24. Neuberger, T.; Schopf, B.; Hofmann, H.; Hofmann, M.; von Rechenberg, B. J. Magn.
Magn. Mater. 2005, 293, 483e496.
25. del Campo, A.; Sen, T.; Lellouche, J.-P.; Bruce, I. J. J. Magn. Magn. Mater. 2005,
293, 33e40.
26. Saiyed, Z. M.; Sharma, S.; Godawat, R.; Telang, S. D.; Ramchand, C. N. J. Biotechnol.
2007, 131, 240e244.
27. Sayin, S.; Ozcan, F.; Yilmaz, M. Desalination 2010, 262, 99e105.
28. Ediz, O.; Tabakci, M.; Memon, S.; Yilmaz, M.; Roundhill, D. M. Supramol. Chem.
2004, 16, 199e204.
ꢂ
ꢂ
29. Stastny, V.; Lhotak, P.; Michlova, V.; Stibor, I.; Sykora, J. Tetrahedron 2002, 58,
7207e7211.
€
30. Deligoz, H.; Yilmaz, M. J. Polym. Sci., Part A: Polym. Chem. 1995, 33, 2851e2853.
31. Akkus¸ , G. U.; Memon, S.; Sezgin, M.; Yilmaz, M. Clean: Soil, Air, Water 2009, 37,
109e114.
32. Roundhill, D. M.; Koch, H. F. Chem. Soc. Rev. 2002, 31, 60e67.
33. Shinkai, S. Pure Appl. Chem. 1986, 58, 1523e1528.
34. Shinkai, S.; Shiramama, Y.; Satoh, H.; Manabe, O. J. Chem. Soc., Perkin Trans. 2
1989, 1167e1171.
35. Gutsche, C. D.; Nam, K. C. J. Am. Chem. Soc. 1988, 110, 6153e6162.
36. Collins, M.; McKervey, M. A.; Madigan, E.; Moran, M. B.; Owens, M.; Ferguson,
G.; Harris, S. J. J. Chem. Soc., Perkin Trans. 1 1991, 3137e3142.
37. Li, Z.-T.; Ji, G.-Z.; Zhao, C.-X.; Yuan, S.-D.; Ding, H.; Huang, C.; Du, A.-L.; Wei, M. J.
Org. Chem. 1999, 64, 3572e3584.
4.5. Selectivity studies
4.5.1. Anion selectivity studies. Selectivity studies of 4e7 were
performed in the presence of different sodium salts nitrate (NO3ꢀ),
sulfate (SO42ꢀ) and chloride (Clꢀ) anions since they could be present
more than dichromate anions in aqueous solutions. For this pur-
pose, anions were used as corresponded with one hundred-fold of
dichromate anion concentration and determined according to the
literature.2
38. Negus, S. S.; Baumann, M. H.; Rothman, R. B.; Mello, N. K.; Blough, B. E. J.
Pharmacol. Exp. Ther. 2009, 329, 272e281.
39. Jaime, C.; de Mendoza, X.; Prados, P.; Nieto, P. M.; Sanchez, J. Org. Chem. 1991,
56, 3372e3376.
40. Memon, S.; Roundhill, D. M.; Yilmaz, M. Collect. Czech. Chem. Commun. 2004, 69,
1231e1250.
41. McKinley, J. P.; Zachara, J. M.; Smith, S. C.; Turner, G. D. Clays Clay Miner. 1995,
43, 586e598.
4.5.2. Cation selectivity studies. Selectivity studies of 4e7 were
performed in the presence of Fe3þ, Ca2þ, Kþ and Naþ cations since
they could be present more than uranyl cation in aqueous solutions.