C O M M U N I C A T I O N S
stoichiometric manner to the amount of Hg2+. The selectivity of
this system for Hg2+ over other metal ions is remarkably high, and
its sensitivity is below 2 ppb in aqueous solutions. The findings
suggest that this method will serve as the foundation of practical
chemodosimeters for rapidly determining Hg2+ concentrations in
aqueous environments.
Acknowledgment. This work was supported by the Center for
Bioactive Molecular Hybrids (CBMH) at Yonsei University.
Supporting Information Available: Experimental procedures for
the synthesis, spectral data, and copies of 1H NMR and 13C NMR of 1
and 4, data for UV-vis and fluorescence titrations of 1. This material
Figure 2. Fluorescence spectra (excitation at 500 nm) of 1 (1 µM) in
water-methanol (80/20 v/v) at pH 7 in the presence of 1 equiv of Hg2+
,
,
Ag+, Zn2+, Cu2+, Pb2+, Cd2+, Ni2+, Co2+, Fe2+, Mn2+, Mg2+, Ca2+, Ba2+
Li+, K+, Na+, Rh3+, Cr2+
.
References
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Figure 3. Color changes of 1 (10 µM) upon addition of Hg2+, Ag+, Cu2+
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,
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Figure 4. (a) Fluorescence emission changes of 1 (10-7 M) upon additions
of Hg2+ (by 1 ppb) in water-methanol (80/20 v/v) at 25 °C. (b) The
fluorescence intensities at 556 nm.
Changes in the fluorescence properties of 1 caused by other metal
ions, including Ag+, Zn2+, Cu2+, Pb2+, Cd2+, Ni2+, Co2+, Fe2+
,
Mn2+, Mg2+, Ca2+, Ba2+, Li+, K+, Na+, Rh3+, Cr2+, were also
measured. Fluorescence spectra of solutions of 1 (1 µM), recorded
within 5 min after the addition 1 equiv of each of these metal ions,
are displayed in Figure 2. Only Ag+ and Zn2+ ions promote small
fluorescence intensity changes,12 while other metal ions did not
cause any significant changes under identical conditions. The
selectivity observed for Hg2+ over other ions is remarkably high.
In addition, the enhancement in fluorescence intensity resulting from
addition of Hg2+ is not influenced by subsequent addition of other
metal ions. Finally, while the colorless to pink color change
associated with the reaction of 1 with Hg2+ is readily detectable
visually, no significant color changes are promoted by other metal
ions (Figure 3).
(7) (a) Wang, X.; Li, Z.; Wei, B.; Yang, J. Synth. Commun. 2002, 32, 1097-
1103. (b) Zou, X.; Jin, G. J. Heterocycl. Chem. 2001, 38, 993-996.
(8) Yang, X.-F.; Guo, X.-Q.; Zhao, Y.-B. Talanta 2002, 57, 883-890.
(9) The spirocyclic form was confirmed by 13C NMR spectra. The spiro carbon
peak appeared at 67.0 ppm. According to the pH titration, compound 1
retained the spirocyclic form in the pH range of 4-14. Below pH 4, the
fluorescence intensity increased, which implies that ring opening is
occurring. Compound 1 is stable as a solid and a solution for several
days.
To see practical applicability, the detection limit of this new
chemodosimeter system was evaluated. The fluorescence titration
profile of 1 (10-7 M) with Hg2+, shown in Figure 4, demonstrates
that detection of Hg2+ is at the parts per billion level.13 Under these
conditions, the fluorescence intensity of the solution of 1 was nearly
proportional to the amount of Hg2+ added (Figure 4b).
In summary, the investigation described above has resulted in
the development of a highly selective and sensitive chemodosimeter
for Hg2+ ion in aqueous solution. The system, which utilizes an
irreversible Hg2+-promoted oxadiazole forming reaction of rhodamine
derivative 1, is monitored by colorimetric and fluorescence intensity
changes that respond instantaneously at room temperature in a 1:1
(10) Typical desulfurization reactions used in known Hg2+ chemodosimeters
require elevated temperatures and/or relatively long reaction times.
(11) The fluorescence quantum yield was calculated using Rhodamine 6G (Φf
) 0.94 in EtOH) as a reference (Fischer, M.; Georges, J. Chem. Phys.
Lett. 1996, 260, 115-116).
(12) Fluorescent intensities promoted by Ag+ increased gradually over an 8 h
period.
(13) The EPA standard for the maximum allowable amount of Hg2+ in drinking
water is 2 ppb.
JA054855T
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J. AM. CHEM. SOC. VOL. 127, NO. 48, 2005 16761