ChemComm
Communication
In brief, we have reported a unique reagent that is capable of
À
detecting CN either in a pure aqueous environment at a
concentration lower than the safe limit of environmental
primary standards or in live HeLa cells pre-exposed to aqueous
À
solution with [CN ] of 0.2 ppm, the permissible limit set by
the world regulatory body for safe drinking water. Initial
studies clearly reveal that 1ÁCu could be used to develop a
phosphorescence turn-on assay for studying the enzymatic
activity of HNL on a cyanohydrin compound. No such example
was reported earlier using a receptor for cyanide.
A.D. acknowledges DST for funding. S.S. and P.D. thank
CSIR, while U.R.G. and M.B. thank UGC for their fellowships.
S.K.G. thanks DBT for partial support and DST for Confocal
facilities at IIT, Kharagpur, India. A.D. thanks Analytical
Science Department and CIF for help with various analytical
and spectroscopic analysis.
Fig. 3 (A) Emission spectra of (a) 1ÁCu, (b) HNL, (c) 1ÁCu + mdnl + HNL; {(c) À (b)}
was generated after subtracting the spectra of HNL (b) from the spectra of the
solution having 1ÁCu + mdnl + HNL (c) to nullify the emission due to the HNL.
[
{
(
1ÁCu] = 0.02 mM, [mdnl] = 0.8 mM, [HNL] = 10 mL; (B) emission spectra of
1ÁCu (0.02 mM) + mdnl (0.8 mM)} in the absence and presence of varying [HNL]
0–75 mL). Aq. HEPES buffer (pH 6.5) was used for all studies.
HeLa cells (cervical cancer cells) pre-exposed to a buffer
solution (pH 7.6) of 5 mM 1ÁCu. To examine such a possibility, Notes and references
pre-treated live HeLa cells were exposed to various [NaCN]
1
C. Young, L. Tidwell and C. Anderson, Cyanide: Social, Industrial,
(
0.2 to 1.0 ppm) in aq. HEPES buffer medium (pH 7.6) and were
and Economic Aspects, Minerals, Metals, and Materials Society,
Warrendale, 2001.
R. M. Glead, W. J. Foley and I. E. Woodrow, Plant, Cell Environ.,
visualized under a laser scanning confocal microscope (Fig. 2).
The micrographs of the loaded cells displayed a distinct
increase in the intracellular emission intensity in the red
2
1998, 21, 12.
3 Guidelines for Water Reuse, U.S. Environmental Protection Agency,
EPA/625/R-04/108-2004, Washington, DC.
(a) Y. Asano1, M. Dadashipour, M. Yamazaki, N. Doi and H. Komeda,
Protein Eng., Des. Sel., 2011, 24, 607; (b) R. J. H. Gregory, Chem. Rev.,
1999, 99, 3649.
(a) S.-S. Sun and A. J. Lees, Chem. Commun., 2000, 1687; (b) H. Miyaji
and J. L. Sessler, Angew. Chem., Int. Ed., 2001, 40, 154; (c) S. Saha,
A. Ghosh, P. Mahato, S. Mishra, S. K. Mishra, E. Suresh, S. Das and
A. Das, Org. Lett., 2010, 12, 3406.
À
channel (590 Æ 10 nm) with an increase in the [CN ]. Higher
4
À
[CN ] accounted for the regeneration of the luminescent
complex (1) from the nonluminescent binuclear complex 1Á
Cu, which accounted for the enhanced cellular emission. No
significant change of the cell morphology or floating appearance of
the cells was observed. Further, images shown in Fig. 2 confirmed
the cell membrane permeability of the 1ÁCu reagent as well as the
possibility of using this reagent for the intracellular distribution of
CN as low as 0.2 ppm, the [CN ] set by the U.S. EPA for safe
drinking water. This is significant in the context of the total scenario
for the CN ion detection in an aqueous environment, as there are
5
6
(a) K.-S. Lee, H.-J. Kim, G.-H. Kim, I. Shin and J.-I. Hong, Org. Lett., 2008,
1
0, 49; (b) H.-J. Mo, Y. Shen and B.-H. Ye, Inorg. Chem., 2012, 51, 7174;
c) M. Schmittel and S. Qinghai, Chem. Commun., 2012, 48, 2707.
7 (a) Y. H. Kim and J.-I. Hong, Chem. Commun., 2002, 512;
b) P. Anzenbacher, D. S. Tyson, K. Jursikova and F. N. Castellano,
(
À
À
(
J. Am. Chem. Soc., 2002, 124, 6232.
À
8
(a) S. Y. Chung, S. W. Nam, J. Lim, S. Park and J. Yoon, Chem.
Commun., 2009, 2866; (b) X. Chen, S. Nam, G. Kim, N. Song,
Y. Jeong, I. Shin, S. K. Kim, J. Kim, S. Park and J. Yoon, Chem.
Commun., 2010, 46, 8953; (c) K. P. Divya, S. Sreejith, B. Balakrishna,
P. Jayamurthy, P. Anees and A. Ajayaghosh, Chem. Commun., 2010,
6069; (d) H. S. Jung, J. H. Han, Z. H. Kim, C. Kang and J. S. Kim, Org.
Lett., 2011, 13, 5056; (e) V. Bhalla, H. Singh and M. Kumar, Dalton
Trans., 2012, 41, 11413.
(a) G. Eaton, A. S. Pena-Nu n˜ ez, M. C. R. Symons, M. Ferrario and
I. R. McDonald, Faraday Discuss. Chem. Soc., 1988, 85, 237; (b) G. J. Kim
and H. J. Kim, Tetrahedron Lett., 2010, 51, 185; (c) J. H. Lee, A. R. Jeong,
I. S. Shin, H. J. Kim and J. I. Hong, Org. Lett., 2010, 12, 764; (d) S. Park
and H. J. Kim, Chem. Commun., 2010, 46, 9197.
À
only two earlier references that describe the CN detection as low
as 0.013 ppm and 3.25 ppm in 99.95% (0.5%, CH CN) and 99%
3
8b,d
(1% DMSO) aqueous environment, respectively.
The other two
À
articles, which describe the CN detection in pure water medium,
have reported relatively higher detection limits.
We also explored the possibility of using the 1ÁCu reagent for
probing the in situ cyanide generation following an enzymatic
process initiated by HNL, an enzyme that was known to catalyze
the decomposition of mandelonitrile (mdnl) and liberate
11
9
cyanide at pH 6.5, and thus to develop a turn-on assay. Fig. 3 10 (a) Y. Liu, X. Lv, Y. Zhao, J. Liu, Y.-Q. Sun, P. Wang and W. Guo,
J. Mater. Chem., 2012, 22, 1747; (b) J. Rosenthal and S. J. Lippard,
J. Am. Chem. Soc., 2010, 132, 5536.
1 (a) A. Touceda-Varela, E. I. Stevenson, J. A. Galve-Gasion, D. T. F.
reveals that HNL has an inherent emission band with maxima
at 437 and 453 nm in aq. HEPES buffer medium of pH 6.5. A
1
distinct increase in emission intensity at B583 nm with an
increase in [HNL] in the solution mixture containing mdnl and
Dryden and J. C. Mareque-Rivas, Chem. Commun., 2008, 1998;
(
b) F. Garc ´ı a, J. M. Garc ´ı a, B. Garc ´ı a-Acosta, R. Mart ´ı nez-M ´a n˜ ez,
F. Sancen ´o n and J. Soto, Chem. Commun., 2005, 2790.
2 (a) A. B. Tamayo, B. D. Alleyne, P. I. Djurovich, S. Lamansky, I. Tsyba,
N. N. Ho, R. Bau and M. E. Thompson, J. Am. Chem. Soc., 2003,
1
ÁCu suggests an increase in the formation of 1 and thus, the
1
enhanced in situ generation of cyanide species with higher
125, 7377; (b) Y. You and W. Nam, Chem. Soc. Rev., 2012, 41, 7061.
[
9
HNL] (Fig. 3B). We could evaluate the Michaelis constant (K
.99 Â 10 M) from the plot of v (v being the overall rate
=
m
1
3 (a) Y. You, S. Lee, T. Kim, K. Ohkubo, W.-S. Chae, S. Fukuzumi,
G.-J. Jhon, W. Nam and S. J. J. Lippard, J. Am. Chem. Soc., 2011,
133, 18328; (b) P.-K. Lee, W. H. T. Law, H. W. Liu and K. K.-W. Lo,
Inorg. Chem., 2011, 50, 8570; (c) K. K.-W. Lo, P.-K. Lee and J. S. Y.
Lau, Organometallics, 2008, 27, 2998; (d) J. Liu, Y. Liu, Q. Liu, C. Li,
L. Sun and F. Li, J. Am. Chem. Soc., 2011, 133, 15276.
À4
constant) vs. 1/[mdnl] ([mdnl] = 0.5 mM to 50 mM), while [HNL]
(
moderately low value of K
À5
30 mL) and [1ÁCu] (2.0 Â 10 M) were kept unchanged.† A
m
implies that the enzyme has a
moderately high affinity for the substrate mandelonitrile.
14 M. Suresh, A. Ghosh and A. Das, Chem. Commun., 2008, 3906.
This journal is c The Royal Society of Chemistry 2013
Chem. Commun., 2013, 49, 255--257 257