Full Paper
Conclusion
We have designed and synthesized a new sulfinyl xanthene de-
rivative that can act as a simultaneous dual sensor of different
analytes, such as biological biothiols and phosphate anions.
The mechanism of action of this derivative implies thiolysis of
the sulfinyl group of the weakly fluorescent DNBS-GG by bio-
logical biothiols, thus releasing a fluorescent GG moiety that si-
multaneously responds to phosphate anions through its fluo-
rescence-decay time. The efficiency of this new dye as a dual
sensor was probed in experiments at two significant pH values
in vitro; that is, pH 9, at which the probe responds faster and
is more sensitive to biothiols, and pH 7.35, which is required
for biological applications. In both cases, we could detect the
presence of cysteine, homocysteine, or glutathione and deter-
mine the phosphate-ion concentration at the same time. Note
that this probe is suitable for thiol detection in cases of cellular
stress due to its low response to ROS. Moreover, this new dye
was tested intracellularly by using FLIM in HeLa cells and
showed permeability through the cell membrane. Again, the
increase in the fluorescence intensity confirmed the ability of
this dye to detect thiols, and changes in the fluorescence life-
time enabled its behavior as a phosphate-ion concentration
sensor.
Figure 5. A) FLIM images of cells incubated with a-toxin and with DNBS-GG
(110À7 m) at pH 7.35 with phosphate-ion concentrations of 0, 100, and
200 mm (arbitrary color scale). The FLIM images were collected after 30 mi-
nutes to allow the reaction of DNBS-GG with the intrinsic thiols. Scale bar
represents 10 mm. B) Recovered lifetime of DNBS-GG in a-toxin-treated cells
in the presence of different phosphate-ion concentrations. Error bars repre-
sent standard deviations from the measurements of at least five different
images containing multiple cells.
to the extracellular media. Along with the increase in the fluo-
rescence emission due to a reaction with the internal thiols,
the FLIM images show changes in the fluorescence lifetime of
the probe because of the changes in the total phosphate-ion
concentration (Figure 5A,B). Previously,[24] we have reported
the kinetic rate constant of the buffer-mediated proton-trans-
fer reaction in the ground state in different buffers by using
fluorescence correlation spectroscopy (FCS) and showed that
only a suitable buffer, such as phosphate, makes the reaction
fast enough to compete with fluorescence emission; therefore,
we could assign these changes in lifetime to phosphate ESPT
among other cell species. Although Dt shows a large error bar,
this is intrinsic to cell-to-cell variation. Nevertheless, we have
shown the excellent feasibility and specificity of this method in
previous reports for following variations of the phosphate-ion
concentration in living cells between 10 and 600 mm.[13;14,29]
We show that this dye can detect thiols and phosphate ions
at the same time. The combined sensing of inorganic phos-
phate ions and GSH has a clear biological relevance. In bone
tissue, the regulation of bone synthesis and degradation is
modulated by oxidative stress. The molecular bases of these
interactions have been proposed, and the role of specific
genes that promote oxidative stress in the development of os-
teoporosis has been described (e.g., the NOX4 gene promotes
oxidative stress and osteoporosis,[30] whereas FoxO1 gene ex-
pression exerts a protective effect).[31] In addition, sensing of
phosphate-based energy-rich compounds and oxidative stress
is relevant in biology in pathological processes that include al-
teration of the energetic metabolism combined with an in-
crease in oxidative stress. Examples of these situations are
cancer,[32] obesity, diabetes,[4] and hypoxia[33]. Studies that use
our dye for some of these biological diseases and sensibility
against phosphate compounds are in progress.
Experimental Section
General
All reactions were performed in dry glassware in an air atmos-
phere. All of the commercially available reagents (2,4-dinitrobenze-
nesulfonyl chloride and 2,4-dinitrobenzenesulfonic acid) and sol-
vents (triethylamine, dichloromethane, and methanol) were used
without further purification. TLC analysis was performed on alumi-
num-backed plates coated with silica gel 60 (230–240 mesh) with
F254 indicator. The spots were visualized with UV light (l=
254 nm) and/or staining with Ce/Mo reagent or phosphomolybdic
acid solution and subsequent heating. NMR spectra were mea-
1
sured at room temperature and the H NMR spectra were recorded
at 500 or 600 MHz.
Synthesis and spectroscopic data of DNBS-GG
2,4-Dinitrobenzenesulfonyl chloride (29 mg, 0.11 mmol) was added
to Granada Green (GG, 20 mg, 0.056 mmol) dissolved in Et3N and
CH2Cl2 (4 mL, 1:1 v/v; Scheme 3). The reaction was monitored by
TLC analysis and 2,4-dinitrobenzenesulfonyl chloride (29 mg,
0.11 mmol) was added every 60 min until no starting material was
observed. The solvent was removed by evaporation, and the resi-
due was purified by flash chromatography with CH2Cl2/MeOH as
the eluent to give the corresponding DNBS-GG derivative as
1
a dark-orange solid (16 mg, 50%). H NMR (600 MHz, [D6]acetone):
d=8.95 (d, J=2.7 Hz, 1H), 8.60 (dd, J=9.2, 2.8 Hz, 1H), 7.66 (d, J=
9.2 Hz, 1H), 7.35 (s, 1H), 7.34 (d, J=2.4 Hz, 1H), 7.29–7.25 (m, 3H),
7.17 (dd, J=8.8, 2.4 Hz, 1H), 7.08 (d, J=9.8 Hz, 1H), 6.44 (dd, J=
9.8, 1.7 Hz, 1H), 6.16 (d, J=1.7 Hz, 1H), 3.82 (s, 3H), 1.44 ppm (s,
9H); 13C NMR (151 MHz, [D6]acetone): d=187.1 (C), 161.1 (C), 160.9
(C), 159.5 (C), 157.9 (C), 156.2 (C), 148.1 (C), 146.1 (C), 143.7 (C),
133.7 (CH), 133.2 (CH), 133.0 (CH), 132.8 (CH), 132.1 (CH), 130.2 (C),
124.8 (CH), 124.6 (CH), 123.2 (C), 121.0 (C), 120.9 (C), 120.5 (CH),
118.3 (CH), 111.7 (CH), 109.4 (CH), 107.9 (CH), 57.8 (CH3), 37.7 (C),
Chem. Eur. J. 2015, 21, 14772 – 14779
14777
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