recent developments in rhodamine salicylidene hydrazone chemosensors
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standards and chemosensors.13,14 Rhodamine spirocyclic che-
mosensors have attracted a lot of attention due to their
simplicity, high sensitivity, and real-time detection for various
analytes in vivo and in vitro.15–18 The preferential binding sites
are spiro-carbonyl O, imide N and other N or O sites such as
ortho-phenol O. However, their selectivity properties to analytes
are strongly inuenced by the structure, substituents, solvent
and temperature.19 Hence a subtle change in the rhodamine
binding sites might aff ect the “spirolactam ring-opening ”process which could modify their selectivity and sensitivity
(Fig. 1).20
2. Detection of analytes based onrhodamine salicylidene hydrazone2.1 Sensors for detecting Cu2+
The copper ion is an essential trace element in biological
systems, and plays as a catalytic cofactor for a variety of met-
alloenzymes in the lifecycle.21 Therefore, a convenient and fast
method to detect Cu2+ existing in environmental and biological
resources is of considerable importance. However, it was not
until 2006 that Tong's group reported the rst salicylidene
rhodamine hydrazone chemsensor RhB-Sal (1) and applied it to
the detection of Cu2+ ions in neutral buff ered media.22 In their
study, the rhodamine chemsensor 1 displayed a reversible
absorption and uorescence enhancement response to Cu2+ via
a 1 : 1 binding mode. Furthermore, the sensitivity of 1 for Cu2+
can be lower than 25 nM in 50% (v/v) buff ered water/CH3CN by
the absorption spectra method and the 0.1 mM level for the
uorescence method under these conditions. Even in neutral
buff ered aqueous solutions, the uorescence method was
successful in sensing Cu2+ at a micromolar level.
Ma et al. have designed and synthesized a rhodamine-baseduorescent probe 2 for copper ions.23 Probe 2 exhibited high
sensitivity toward Cu2+ and about a 37-fold increase in uo-
rescence emission intensity, which was observed upon the
addition of 10 equiv. of Cu2+ in 50% water–ethanol buff ered at
pH 7.10. Besides, upon binding Cu2+, a remarkable color
change from colorless to pink was easily observed by the naked
eye. The linear response range covered a concentration range of
Cu2+ from 8.0 107 to 1.0 104 mol L1 and the detection
limit was 3.0 107 mol L1. Except for Co2+, the probe
exhibited high selectivity for Cu2+ over a large number of
coexisting ions. It has been used for direct measurement of Cu2+
content in environmental and biological systems.
Tang's group designed a rhodamine B based derivative 3 as
a colorimetric and uorescent dual mode sensor for recognition
of Cu2+
in CH3CN/H2O (1 : 1, v/v, HEPES 10 mM, pH ¼ 7.0)solution.24 Sensor 3 displayed highly selective, sensitive and
rapid recognition behavior toward Cu2+ among a range of bio-
logically and environmentally important metal ions. The 1 : 1
binding stoichiometry of 3 and Cu2+ was proved by nonlinear
least-squares tting of titration proles and Job's plot; the
association constant and uorescence detection limit were
calculated to be 1.92 106 M1 and 7.96 108 M, respectively.
The Cu2+ recognition process was reversible and showed little
interference from other coexisting metal ions.
Chen and co-workers synthesized a salicylidene rhodamine
chemosensor 4 through the reaction of rhodamine hydrazide
and salicylaldehyde receptor.
25
It exhibited a reversible andsensitive “turn-on” response of absorption and uorescence
toward Cu2+ in aqueous acetonitrile solution. An approximate
65 and 6-fold enhancement in the absorbance at 556 nm and
uorescence intensity at 573 nm were estimated when the
concentration of Cu2+ reached 10 mM. 4 displayed more sensi-
tivity than the known compound RhB-Sal for Cu2+ (ca. 30 and
2-fold, respectively) under the same conditions. The competi-
tion experiments for Cu2+ mixed with common metal ions
exhibited no obvious change in absorption and emission except
for Cr3+ ion, which could induce uorescence quenching to
a certain extent.
Yang's group developed a colorimetric and uorescent
sensor 5 by the condensation reaction of rhodamine B hydra-zide and 2,4-dihydroxybenzaldehyde, which showed reversible
and highly selective and sensitive recognition toward Cu2+ over
other examined metal ions.26 Upon addition of Cu2+, sensor 5
exhibited remarkably enhanced absorbance intensity and color
change from colorless to pink in a DMSO and MeCN aqueous
Jinglin Liu received his Ph.D.
degree in 2006 under the guid-
ance of Prof. Xu Bai and Prof.
Hengbin Zhang from Jilin
University. He began his inde-
pendent research career at
NENU in 2007. He was
promoted to a full professor in
the college of chemistry and
chemical engineering of IMUN in
2012. His current research
interests involve combinatorial
chemistry and organic synthesis
methodology.
Dewen Dong received his PhD in
1999 from Changchun Institute
of Applied Chemistry of CAS,
and then he became a Lecturer
in Shizuoka University (1999–
2001) and a postdoctoral fellow
in the University of Hull (2001–
2003). He joined the faculty of
NENU as a full professor in 2003
and moved to Changchun Insti-
tute of Applied Chemistry of CAS
as a professor in 2006. His
research includes synthetic
chemistry and functional
organic/polymeric materials.
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buff er solution or pure MeCN, and showed signicant off –on
uorescence accompanied by color changes from colorless to
orange in MeCN. In DMSO/Tris–HCl buff er (1 : 9, v/v, pH 7.0)
solutions, the quantication of Cu2+ by 5 was satisfactory in
a linear working range of 10–300 mM, with an absorbance
detection limit of 3.42 106 M. The sensor 5 was also
successfully applied to the determination of Cu2+ in water
samples.
Gupta and co-workers also synthesized the rhodamine-
derived Schiff base 6 and investigated its sensing behavior by
UV-vis and uorescence spectroscopic techniques.27 The sensor
exhibited a highly selective and sensitive colorimetric response
Table 1 The comparison of the
uorescence probes for Cu
2+
based on salicylidene
Structure Media AnalyteDetectionlimit
Working range
Associationconstant
Detectionmode Probe ref.
CH3CN/H2O,Tris–HCl, pH ¼ 7.0
Cu2+ 25 nM, 0.1 mM 0–10 mM 6.91 104 Abs, FL 1 (ref. 22)
EtOH/water,Tris–HCl, pH ¼ 7.1
Cu2+ 0.3 mM 0.8–100 mM — FL 2 (ref. 23)
CH3CN/H2O,HEPES, pH ¼ 7.0
Cu2+ 7.96 108 0–10 mM 1.92 106 Abs, FL 3 (ref. 24)
CH3CN/Tris–HCl,pH ¼ 7.0
Cu2+ 10 mM,
naked eye 0–20 mM 3.09 104 Abs, FL 4 (ref. 25)
DMSO/Tris–HCl,pH ¼ 7.0
Cu2+ 3.42 106 10–300 mM 2.83 104 Abs, FL 5 (ref. 26)
CH3OH/H2O Cu2+, Al3+,
Fe3+ 0.99 108 0–20 mM 1.1 106 Abs 6 (ref. 27)
CH3OH/HEPES,pH ¼ 7.0
Cu2+, VO2+ 106 to 105,
naked eye 0–80 mM — Abs 7 (ref. 28)
CH3CN/H2O Cu2+, Hg 2+ 105 10–100 mM — Abs, FL 8 (ref. 29)
CH3OH/HEPES,pH ¼ 7.0
Cu2+ 3.7 108 0–5 mM — Abs 9 (ref. 30)
CH3OH/HEPES,pH ¼ 7.0
Cu2+ 1.2 109 0–20 mM — Abs, FL 10 (ref. 30)
Dry CH3CN Cu2+ 0.49, 14.98 mM 0–20 mM
6.72 104,4.23 104
Abs, FL 11 (ref. 31)
CH3CN/HEPES,pH ¼ 7.04
Cu2+ 0.20 mM 0–20 mM 3.7 104 Abs, FL 12 (ref. 32)
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to Cu2+ and Al3+, and an “off –on” uorescence response toward
Fe3+ in semi-aqueous media. The spectral changes obtained are
large enough in the visible region of the spectrum and thus
enable naked-eye detection. The 1 : 1 stoichiometric ratio
between probe and metal ions was proposed based on a Job's
plot, which was further conrmed by ESI mass analysis. Paper
strips were also used for the detection of Cu2+, Al3+ and Fe3+
ions.
Huo et al. synthesized a rhodamine-based colorimetric che-mosensor by incorporating rhodamine hydrazide and 5-chlor-
osalicylaldehyde in ethanol. The sensor 7 exhibited specic
absorbance responses to Cu2+ and turned from colourless to
purple red, which allowed naked-eye detection of Cu2+ ions in
50% CH3OH–H2O solution.28 The low detection threshold for
Cu2+ in UV-vis spectrum was 106 to 105 M and at this level the
color change was very obvious. In contrast, the selectivity
towards VO2+ was determined from changes in the emission
spectra in the nanomolar range. This represents the rst re-
ported rhodamine-based sensor capable of detecting both Cu2+
and VO2+ using two diff erent modes.
Yang and co-workers reported a rhodamine salicylidenehydrazone derivative 8 by condensation of 3,5-dichlor-
osalicylaldehyde and rhodamine B hydrazide. The sensor 8 was
utilized as a colorimetric and reversible chemosensor for Cu2+
and Hg 2+ in aqueous CH3CN media.29 Among the various metal
ions, the sensor 8 exhibited remarkably enhanced absorbance
intensity and color change for Cu2+, and showed signicant
“off –on” uorescence accompanied with red emission upon
binding with Hg 2+. The absorbance and uorescence signals of
8 could be restored with addition of EDTA into solutions of 8-
Cu2+ and 8-Hg 2+, indicating that the binding process is chemi-
cally reversible.
Huo's group synthesized two salicylidene-based rhodamine
derivatives 9 and 10.30 Because of their diff erent salicylidene
groups, 9 exhibited particular selectivity towards Cu2+ with color
changes from colorless to yellow, which can be used as a UV-vischemosensor for Cu2+. Due to the strong intramolecular charge
transfer, 9 was very weakly uorescent and the 9-Cu2+ metal
complex remains non-uorescent. The absorbance intensity of
9 was linearly proportional to Cu2+ concentrations of 0–5 mmol L1
with a detection limit of 3.7 108 M. Diff erent from the
process of 9, the sensor 10 was strongly uorescent, which can
be used as a dual-channel colorimetric and uorescent
compound for Cu2+. The uorescence detection limit of 10 to
Cu2+ is 1.2 109 M, which was more sensitive than the UV-vis
behavior of 9. The cell experiments show the good cell-
membrane permeability of compound 10, and it can thus be
used to mark Cu
2+
within living cells. A new rhodamine derivative 11 bearing an electron with-
drawing group –NO2 at the 5-position of the 2-hydroxyphenyl
moiety was synthesized by Chen et al.31 The sensor displayed
similar high selectivity for Cu2+ over coexisting metal ions
except that Fe3+ brought about some absorption interference
and Bi3+ led to a little uorescence interference. The detection
Table 2 The comparison of the uorescence probes for Cu2+ from naphthaldehyde and rhodamine 6G
Structure Media AnalyteDetectionlimit
Working range
Associationconstant
Detectionmode Probe ref.
CH3CN/HEPES,pH ¼ 7.04
Cu2+ 0.2 mM 0–20 mM 5.0 104 Abs, FL 13 (ref. 32)
CH3CN/H2O Cu2+ 0.32 ppb 0–5 mM 5.4 105 Abs 13 (ref. 33)
CH3CN/HEPES,pH ¼ 7.4
Cu2+ 0.156 mM 0–4 mM — FL 15 (ref. 34)
CH3CN/HEPES,pH ¼ 7.04
Cu2+ 0.2 mM 0–20 mM 5.6 105 Abs, FL 14 (ref. 32)
CH3CN/HEPES,pH ¼ 7.4
Cu2+ — 0–200 mM 2.5 104 Abs, FL 16 (ref. 35)
EtOH/H2O, NaAc–HAc,pH ¼ 7.0
Cu2+ 10 nM,
25 nM 0–5 mM 1 106 Abs, FL 17 (ref. 36)
CH3CN/H2O,pH ¼ 7.0
Cu2+ 5 mM,
naked eye 0–50 mM 4.877 104 Abs, FL 18 (ref. 37)
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limit for Cu2+ calculated from the uorescence titration data
was 0.49 mM. The sensitivity of 11 for Cu2+ in pure CH3CN is
higher than aqueous solutions. The sensor 11 was expected to
reversibly bind to Cu2+ in each medium, forming a 1 : 1 stoi-
chiometric 12-Cu2+ complex with an association constant of
6.72 104 M1 and 4.23 104 M1, respectively (Table 1).
Wang and co-workers reported three rhodamine-salicylidene
derivative 12, rhodamine-naphthalene derivative 13 and
rhodamine-binaphthol derivative 14 as specic uorescent andcolorimetric chemosensors for Cu2+.32 These probes exhibited
selective “off –on” type changes in both absorption and emis-
sion spectra toward Cu2+ ions compared to other metal ions.
The detection limits of 12, 13 and 14 toward Cu2+ were all 0.20
mM (12.7 ppb) by plotting the uorescence intensity at 571 nm
versus the concentration of Cu2+. The Job's plots indicated a 1 : 1
stoichiometry between 12, 13 or 14 and Cu2+. The association
constants were 3.7 104 M1, 5.0 104 M1 and 5.6 105 M1
respectively, which suggested that the complex of 14-Cu2+ was
more stable than that of 12-Cu2+ and 13-Cu2+.
Wu's group reported a rhodamine-based 2-hydroxy-1-naph-
thaldehyde hydrazone chemosensor 13, which showeda reversible, selective, and sensitive absorbance enhancement
response to Cu2+ in a buff ered CH3CN–H2O media.33 The probe
13 had a linear response to increasing amounts of low Cu2+
concentration (between 5 and 50 nM), establishing that the
system has a limit of quantication down to 0.32 ppb. The
association constant of molecule 13 with Cu2+ was 5.4 105
M1, and the stoichiometry for 13-Cu2+ was calculated to be 1 : 1
by the Job's plot method and assumed by the nonlinear tting
of the titration curve.
Yin and co-workers synthesized a sugar-rhodamine salicyli-
dene uorescent sensor 15, and investigated its properties for
Cu2+ according to the Cu2+ triggered spirolactam ring-opening
mechanism.34 The introduction of a sugar residue into the sal-icylidene part, combined with the solvent eff ect, signicantly
improved its selectivity and sensitivity. The synthesized probe
15 exhibited high selectivity and excellent sensitivity to Cu2+ in
acetonitrile media. The detection limit was 0.15 mM, about 200
times lower than the recommended water quality standard of
Cu2+ ions in drinking water. The probe 15 could be simply,
rapidly, and satisfactorily used to detect the concentration of
Cu2+.
Yoon and co-workers reported a rhodamine-pyrene deriva-
tive 16 as a ratiometric and “naked-eye” sensor for the detection
of Cu2+ ion in neutral buff ered media.35 It displayed a highly
selective and ratiometric
uorescence change and a colori-metric change upon the addition of Cu2+, utilizing the spi-
rolactam (nonuorescent) to ring opened amide (uorescent)
process. The nonlinear tting of the titration curve and the data
of Job's plot from absorption spectra assumed a 1 : 1 stoichi-
ometry for the 16-Cu2+ complex with an association constant of
2.5 104 M1.
Tong ’s group designed another rhodamine chemosensor 17
using salicylaldehyde and rhodamine 6G hydrazine as copper-
chelating and signal-reporting groups.36 The sensor exhibited
selective absorbance enhancement to Cu2+ over other metal
ions at 529 nm, with a dynamic working range of 0.05–5.00 mM
and a detection limit of 10 nM. The linear working range using
17 for Cu2+ was 0.1–3.6 mM and the detection limit was 25 nM.
Both absorptiometric and uorometric methods were applied
for the detection of Cu2+ in three water samples.
A rhodamine 6G based 4-(diethylamino) salicylidene hydra-
zone chemosensor 18 was reported by Liu et al.37 The sensor
exhibited a high selectivity for Cu2+ and could serve as a good
selective naked-eye chemosensor for Cu2+ in CH3CN. The
association constant of 18 with Cu2+
ion was found to be 4.877 104 M1, and a 1 : 1 stoichiometric complexation was
conrmed by the Job's plot. Upon the addition of Cu 2+, the
spirolactam ring of 18 was opened and the solution changed
from colorless to red. Strangely, an unexpected uorescence
quenching was observed upon the addition of 5 equiv. Cu2+,
which is contrary to the uorescence turn-on of most rhoda-
mine based chemosensors (Table 2).
2.2 Sensors for detecting Hg 2+
Hg 2+ is one of the most severe environmental contaminants
because it can cause serious health problems, damaging thecentral nervous and endocrine systems, leading to many
cognitive and motion disorders.38 There are many rhodamine
spirocyclic chemosensors that have been applied for sensing
Hg 2+ in environmental and biological resources.39–45 However,
rhodamine sensors modulated with a salicylidene structure for
real-time monitoring of Hg 2+ in environmental samples are still
greatly needed.46,47
Yoon's group synthesized two rhodamine hydrazone deriv-
atives 19 bearing a thiol group as selective uorescent and
colorimetric chemosensor to Hg 2+.48 The ring-opening process
of spirolactam enables large uorescent enhancement and
colorimetric change upon the addition of Hg 2+. The 2 : 1 stoi-
chiometry between 19 and Hg 2+ was conrmed by Job's plots. A plot of the uorescent intensities of 19 versus the log concen-
tration of Hg 2+ exhibited a linear response in the range of 1 nM
to 1 mM, and the detection limit was 1 nM. The sensor 19 can be
employed for the in vivo imaging of nanomolar concentrations
of Hg 2+.
Zhao et al. also reported that 13 can achieve double-channel
detection of Hg 2+ and Mg 2+ by diff erent binding modes and can
detect Hg 2+ through a visible color change.49 The detection limit
for the sensor was estimated to be 80 nM. The association
constant between 13 and Hg 2+ was determined to be 1.0 105
M1. Selective binding sites of the compound 13 to Hg 2+ and
Mg 2+
caused immediate and remarkable
uorescenceenhancement at 589 nm and 523 nm. Furthermore, this probe
can indirectly detect glutathione and cysteine with good linear
relationships.
Jiang and co-workers found the sensor 13 exhibits extremely
high sensitivity (as low as 2 ppb) and selectivity to Hg 2+ in
methanol solution.50 The association constant of 13 with Hg 2+
was calculated to be 3.9 105 ( R ¼ 0.9966) by using nonlinear
least-squares analysis. Further characterization conrmed
a 1 : 1 complex, which restores the ICT eff ect to show uores-
cence. The excellent biological value of 13 was demonstrated by
the uorescence imaging in living yeast and HeLa cells.
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Jiang et al. developed a highly sensitive and selective Hg 2+
probe 20 by connecting a water soluble receptor group
(sulfonated b-naphthol) and rhodamine B together through
hydrazine hydrate.51 The results illustrated that 20 has excellent
sensitivity and selectivity abilities toward Hg 2+ and reaches as
low as 4 ppb of detection limit in methanol. The 1 : 1 binding
stoichiometry was conrmed by the Job's plot method, and the
association constant for Hg 2+ was estimated to be 4.6 106
M1. These outstanding cell permeablility and compatibility
characteristics conrm that this kind of Hg 2+ probe has great
potential in biological and pharmacological systems.
Ma and co-workers designed a novel functionalized SBA-15
nanosensor with salicylidene based rhodamine hydrazone asthe binding site for Hg 2+.52 The sensor showed uorescence
enhancement selectivity as well as selective coloration toward
Hg 2+. Covalently gra ed 21 onto the inner surface of SBA-15
makes the nanosensor easy to recover and recycle. Job's plot
indicated that 21 coordinated to Hg 2+ in a 1 : 1 binding stoi-
chiometry; the detection limit of 21 for Hg 2+ is about 1.5
108 M. The addition of S2 led to both color and uorescence
fading, indicating the reversibility of the binding between 21
and Hg 2+. Using Hg 2+ and S2 as chemical inputs and the
uorescence intensity signal as output, 21-SBA-15 can be
utilized as an INHIBIT logic gate at the nanoscale level
(Table 3).
2.3 Sensors for detecting other metal ions
Zheng et al. have found that the “old” chemsensor RhB-Sal (1)
could be used for the selective and sensitive detection of CrO42
in acidic conditions.53 Based on the special oxidation reaction
with potassium dichromate to produce a highly uorescent
rhodamine B, the uorescence enhancement at 591 nm was
linearly well related to the concentration of CrO42 from 1.0
108 to 3.0 107 M (0.42–12.6 ng mL1) with a detection limit
of 1.5 109 M (0.063 ng mL1). The proposed method could
act as a simple “naked-eye” probe for selective detection of Cr6+,
and be explored to indicate Cr6+ from Cr2O72 and CrO4
2
anions.
Guchhait and Kar et al. developed a novel turn-on uores-
cent chemosensor based on a rhodamine–dihydroxy-
benzaldehyde conjugate.54 The sensor 22 displayed an excellent
selectivity and high sensitivity toward Al3+ with remarkably
enhanced uorescent intensity by a chelation-enhanced uo-
rescence (CHEF) process and also shows a clear color change
from colorless to deep magenta. Job's plot and TOF-MS analysis
conrmed the 1 : 1 binding stoichiometry between 22 and Al3+
ions, and the association constant calculated from the absorp-
tion titration result was found to be 2.56 103 M1. Under UV light illumination, one can visually detect even 2 108 M Al3+
in aqueous-acetonitrile buff er solution without the aid of any
sophisticated instruments.
Tong et al. found that 4- N , N -diethylamino-salicylidene
rhodamine hydrazone 23 exhibited selective and ratiometric
uorescent response toward Zn2+ over other metal ions in
aqueous ethanol.55 Upon the addition of Zn2+, there was an
obvious color change of the uorescence from dark cyan to
greenish yellow which could be monitored easily by the naked
eye. An association constant of log K a ¼ 5.22 was calculated for
the 1 : 1 metal-to-ligand complex according to the absorption
spectral titration data. The 23-Zn
2+
complex showed its revers-ibility in the presence of EDTA.
Li et al. synthesized a colorimetric and uorescence turn on
chemosensor 24 for the detection of Pb2+ ions.56 The sensor
displayed a highly selective uorescence enhancement (about
550 fold) and colorimetric change from colorless to pink in the
presence of Pb2+ in chloroform–THF (7 : 3). The absorbance at
557 nm was saturated a er 2 equiv. of Pb2+ was added. The
uorescence intensity at 577 nm increased continuously with
the Pb2+ concentration in the range of 106 to 105 mol L1. The
binding stoichiometry between 24 and Pb2+ was estimated to be
1 : 1 by Job's plot. The reversibility of the sensor was further
Table 3 The comparison of the uorescence sensors for Hg2+
Structure Media AnalyteDetectionlimit
Working range
Associationconstant
Detectionmode Probe ref.
CH3CN/H2O Hg 2+ 1 nM 109 to 106 — FL 19 (ref. 48)
CH3OH Hg 2+ 2 ppb 0–300 mM 3.9 105 Abs, FL 13 (ref. 49)
CH3CN Hg 2+
, Mg 2+
80 nM 0–
100 mM 1 105
FL 13 (ref. 50)
CH3OH Hg 2+ 4 ppb 0–8 104 1 106 Abs, FL 20 (ref. 51)
CH3CN/H2O Hg 2+ 15 nM 0–200 mM — Abs, FL 21 (ref. 52)
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conrmed by EDTA experiments. Sensor 24 could be used
potentially for the detection Pb2+ in the environment.
Chen et al. have designed and synthesized a new targetable
uorescent probe 25 by linking a conjugated naphthalene
chromophore to a rhodamine platform and a lipophilic tri-
phenylphosphonium cation.57 The probe could sensitively and
selectively detect mitochondrial Fe3+ in living cells. It exhibited
a pseudo-large Stokes shi on the basis of the FRET mechanism
and excellent selectivity for Fe3+
excluding the interference of other metal ions, especially Cr3+. The stability constant of the
25-Fe3+ complex was calculated to be 2.0 104 M1. The
detection limit of 25 responded to Fe3+ linearly in the
micromolar concentration range, was reasonably estimated to
be 6.93 106 M. Furthermore, a er treatment with EDTA, the
color and uorescent emission intensity changed back, indi-
cating that 25 can be classied as a reversible chemosensor for
Fe3+ (Table 4).
2.4 Detection of CN and amino acids
Many well-designed rhodamine hydrazone cation chemo-sensors could be successfully developed as anionic chemo-
sensors by utilizing the indirect method. Using the ensemble
salicylidene rhodamine hydrazone RhB-Sal and Cu2+ ions, Li's
Table 4 The comparison of the salicylidene probes for other metal ions
Structure Media AnalyteDetectionlimit
Working range
Associationconstant
Detectionmode Probe ref.
H2SO4 buff er CrO42 1.5 nM 0–3 mM — FL 1 (ref. 53)
EtOH/H2O, HEPES,pH ¼ 7.0
Zn2+ 0.05 mM 0–10 mM 1.66 105 Abs, FL 22 (ref. 54)
CH3CN/H2O, HEPES,pH ¼ 7.2
Al3+ 20 nM 0–100 mM 2.56 103 FL 23 (ref. 55)
CHCl3/THF Pb2+
— 0–10 mM — Abs, FL 24 (ref. 56)
EtOH/H2O Fe3+ 6.93 mM 0–50 mM 2 104 FL 25 (ref. 57)
Table 5 The comparison of the metal complex sensors for CN and amino acids
Structure Media Analyte Detection limit Working range Detection mode Probe ref.
CH3CN/H2O, Tris–HCl,pH ¼ 7.0
CN 0.013 ppm 0.1–7 mM Abs 26 (ref. 58)ClO 0.81 mM 0–70 mM Abs 26 (ref. 59)Histidine,protease
— 0–5 mg mL Abs 26 (ref. 60)
EtOH/H2O, Tris–
HCl,pH ¼ 7.1 Cysteine 0.14 mM 0
–28 mM Abs, FL 27 (ref. 61)
CH3CN/H2O CN 0.72 nM 0–10 mM Abs, FL 28 (ref. 62)
THF–CH2Cl2 solid state UV — — Abs 29 (ref. 63)
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group designed an indirect anionic chemosensor for
cyanide.58 Upon the addition of trace CN, the magenta color
faded to colorless immediately, with a detection limit as low
as 0.013 ppm, much lower than the maximum contaminant
level for cyanide in drinking water (0.2 ppm). Later they
developed the rhodamine chemosensor 1 as a new type of
probe for the detection of ClO based on the oxidation
property of hypochlorites and diff erent coordinating prop-
erties of Cu+
and Cu2+
.59 Upon the addition of trace ClO
, thecolorless solution turned magenta to report the concentra-
tion of the present hypochlorite ions, with the detection limit
as low as 8.1 107 M in real water samples. They also
proposed an indirect approach to utilize sensitive colori-
metric sensor 26-BSA to detec sensitivelyt a-amino acids.60 As
the hydrolysis of bovine serum albumin (BSA) with the aid of
trypsin produces a-amino acids, the complex of 26-BSA could
act as a label-free, sensitive, selective sensor toward trypsin.
The detection process could be visually observed by the
naked eye.
Using the chemosensing ensemble method, Yang et al.
developed a
uorescent chemosensing ensemble 27 for thedetection of cysteine based on the uorescence inner lter
eff ect.61 Upon adding cysteine to the above solution, the
complexation of Cu2+ and cysteine led to the dissociation of 27,
which thus decreases the uorescence inner lter eff ect of the
solution, and leading to the uorescence increase of the che-
mosensing system. The uorescence increase is linear with
cysteine concentration up to 10.0 mM, with a detection limit of
1.4 107 M.
Hu and co-workers reported a selective and sensitive method
to detect aqueous CN based on a rhodamine B hydrazide and
2-tertbutyldimethyl silyloxy benzaldehyde conjugate (RTSB)
and Fe3+ derivative.62 RTSB displayed highly selectivity and
sensitivity to Fe3+ with uorescence emission enhancement at 581 nm accompanied by a color change from colorless to pink.
In response to CN, the system 28 provides a remarkable
uorescence intensity change, blue shi and also a clear color
change from pink to colorless. The background anions show
small or no interference with the detection of CN. The detec-
tion limit of the system for CN was around 7.2 108 M.
Treatment of 28 with CN aff orded a similar NMR spectrum
with that of RTSB alone, which indicated that addition of CN
prompted the dissociation of 28 and the release of free probe
RTSB.
Recently, Tong and Tang et al. developed a new photo-
chromic system based on rhodamine B salicylidene hydrazonemetal complex 29.63 The molecules showed absorption “turn-
on” and uorescence “turn-off ” response upon UV irradiation
both in solution and in solid matrix. UV light promoted the
isomerization of the salicylaldehyde hydrazone moiety from the
enol-form to the keto-form, and subsequently induced the spi-
rolactam ring-opening in the rhodamine B part and caused the
photochromic reaction. Owing to the good fatigue resistance,
and the tunable lifetime of the ring-open state, 29 was applied
in photo printing and UV strength measurement in the solid
state (Table 5).
3. Conclusions
In this review, we have covered the development and applica-
tions of rhodamine salicylidene hydrazone chemosensors based
on spiroring-opening of the xanthene platform. Considering the
uorophores and structure–activity of the salicylidene group,
most of them display strong selectivity and sensitivity to Cu2+ in
neutral buff ered aqueous solution. From the type of substitu-
ents on the salicylidene group, we found that the electron-donating groups have superior uorescence detection limits to
the electron-withdrawing substituent, in the order of –CH3 >
–OCH3 > –H > –NO2. The detection limits based on the absor-
bance intensity are similar: –OCH3 > H > –F > –Cl > –OH > –NO2.
However, for both ligands and complexes, the presence of an
electron-withdrawing substituent, compared with no substit-
uent on the salicylidene ring, will greatly improve its emission
band or absorption band enhancements and binding capac-
ities. It is noteworthy that the structural modulation of salicy-
lidene is a very powerful approach for other cations, and
application of the indirect sensing strategy is a good idea for the
sensitive detection of anions and other species.Rhodamine salicylidene hydrazone probes play a major role
in pure organic solvent and aqueous organic media, the
combination of rhodamine probes with SiO2 or Fe3O4 nano-
materials and ber polymers, pave a fast and efficient way to the
detection and separation of heavy metal ions in the environ-
ment. Furthermore, the design and implementation of hydro-
philic groups in rhodamine derivatives develops their sensing
abilities in biological imaging and drug delivery. In short, the
development of high selectivity, sensitivity, photostability and
good biocompatibility rhodamine probes will be of great
importance for the environmental and life sciences.
Acknowledgements
The authors gratefully thank the nancial supports of the
National Natural Science Foundation of China (21172211,
21542006, 21362020), the Natural Science Foundation of Inner
Mongolia Autonomous Region, China (2014BS0205) and the
Scientic Research Foundation of Inner Mongolia University for
the Nationalities (NMD1311, NMDGP1403).
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