a sensitive and specific electrochemiluminescent sensor for lead based on dnazyme
TRANSCRIPT
A sensitive and specific electrochemiluminescent sensor for lead based
on DNAzymew
Xi Zhu, Zhenyu Lin,* Lifeng Chen, Bin Qiu and Guonan Chen*
Received (in Cambridge, UK) 8th June 2009, Accepted 6th August 2009
First published as an Advance Article on the web 21st August 2009
DOI: 10.1039/b911191c
A specific ECL sensor for Pb2+ based on DNAzyme has
been developed for the first time; the detection limit of 1.1 �10�11 mol l�1 is much lower than those of fluorescent,
colorimetric or electrical biosensors.
DNAzymes can recognize target analytes or catalyze specific
chemical and biological reactions. Many cofactors, such as
amino acids, nucleic acids, metal ions and small organic
molecules can affect the catalytic activity of DNAzyme, which
makes it a novel platform for developing highly selective
sensors. To date, several DNAzyme sensor studies have been
reported,1–6 and among them, lead-dependent DNAzyme has
been paid much attention, since lead is a common environ-
mental contaminant. Many optical methods have been
developed for Pb2+ sensing based on the behaviour of the
DNAzyme,7–10 but they suffer from possible drawbacks
including the potential for false signals arising from contami-
nating colorants, fluorophores and quenchers. In addition,
cumbersome optical equipment was often needed. In order to
overcome these drawbacks, electrochemical detection methods
combined with DNAzyme have been applied to lead detection.
Xiao et al. developed a Pb2+ electrochemical sensor by
tethering a redox-active group to the DNAzyme and cleaving
the enzyme substrate from the electrode surface.11 Shen et al.
also developed a sensitive electrochemical sensor based on
DNA-Au bio-barcode amplification.12 These initial studies
indicated that electrochemical detection had many advantages
over optical detection, but this research was a first step, and
much more optimization was still needed.
Electrochemiluminescence (ECL) sensors possess the
advantages of both electrochemical and chemiluminescent
sensors, such as high sensitivity, ease of control and the use
of simple equipment.13 Many highly sensitive and selective
ECL DNA sensors have been developed by using high quantum
efficiency ECL labels.14,15 Specially, tris(2,20-bipyridine)-
ruthenium(II) (TBR) and its derivatives have high quantum
efficiencies and their ECL intensities can be further enhanced
by using co-reactors. For example, Miao and Bard employed
TBR as an ECL label and developed an ECL sensor for an
anthrax-related specific DNA sequence with a detection limit
of 30 pM.16 The results showed that the sensitivity of ECL is
much higher than that of electrochemical detection.
In the present work, we describe a DNAzyme-based ECL
sensor for lead, which combines the high selectivity of
DNAzyme with the high sensitivity of ECL. The Pb2+-specific
DNAzyme employed in this study is ‘‘8–17’’ DNAzyme.17,18
Compared with other lead detection methods, this proposed
method has the merits of simpler equipment, higher selectivity
and sensitivity—the sensor has a lower detection limit than
colormetric or electrochemical sensors. In addition, the
proposed methods can be further applied to establish a range
of DNAzyme-based ECL sensors.
The principle of the ECL biosensor for lead is shown in
Fig. 1 (the sequences of the DNA are shown in the ESIw). Thesensor consists of a 50-thiol modified DNA (DNAzyme)
attached to a gold electrode, a 50-amino modified DNA
(DNA substrate strand), and Ru(bpy)32+ N-hydroxyl-
succinimide (TBR-NHS) ester. The DNA substrate strand
can extend on both the 30 and 50 ends as long as the enzyme
recognition portion is reserved. A linker (TTTTT) is inserted
between the thiol group and the DNA-enzyme sequence. The
TTTTT linker extends the DNA above the 6-mercaptohexanol
(MCH) layer for complete hybridization whilst maintaining
DNAzyme activity.7 Thiol modified DNAzymes are
immobilized onto the surface of the gold electrode via
thiol–Au interactions, and the surface density of the
DNAzyme on the gold electrode was about 4.5 �1011 molecules cm�2, as calculated by the method reported
previously.19 The DNA substrate modified with the ECL label
TBR-NHS ester can hybridize with DNAzyme to make a
double-stranded DNA (ds-DNA).
Fig. 1 Principle of the ECL Pb2+ sensor based on DNAzyme.
Ministry of Education Key Laboratory of Analysis and DetectionTechnology for Food Safety, Department of Chemistry,Fuzhou University, Fuzhou, Fujian 350002, China.E-mail: [email protected], [email protected];Fax: +86 591-83713866w Electronic supplementary information (ESI) available: Experimentaldetails, sensor preparation, ECL measurements, optimization ofself-assembly time and the stability of the modified electrode. SeeDOI: 10.1039/b911191c
6050 | Chem. Commun., 2009, 6050–6052 This journal is �c The Royal Society of Chemistry 2009
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When the modified electrode is immersed into a solution
containing Pb2+, the DNAzyme catalyzes the hydrolytic
cleavage of the ds-DNA into two pieces. In this case, the
TBR-NHS ester is removed, which results in the reduction of
the ECL intensity. The ECL intensity decreases with the
increase of Pb2+ concentration. Accordingly, the concentration
of Pb2+ in solution can be obtained indirectly.
The TBR labels were incorporated onto the 50 end of the
DNA substrate using the phosphoramidite method as
previously shown.20 1 OD of DNA substrate was dissolved
in 250 ml of TAE buffer, and then 200 ml of 6.0 � 10�4 mol l�1
Ru(bpy)2(dcbpy)NHS and 10 ml of 0.10 mol l�1 TAE buffer
were added, followed by shaking at low speed overnight at
room temperature. Then, 100 ml of 3 mol l�1 NaAc and 2 ml of
ethanol were added into the mixture, and precipitation was
carried out in a refrigerator over 12 h. The mixture was
centrifuged for 30 min. The precipitate was preserved
and rinsed with cold 70% ethanol solution twice and dried
in air. The dried precipitate was re-dissolved in TAE buffer
(pH 8.2) to obtain the target DNA-TBR solution and stored
at �16 1C.
The incorporation procedure is a relatively reliable method,
its success rate is over 80%.21 We used different concentrations
of standard TBR solutions to get the evolution of the ECL
intensities and the TBR concentrations. Then we detected the
ECL intensities from the modified electrode and calculated the
amount of TBR modified on the electrode. By this method, we
estimate that the amount of Ru(II) labels on the modified
electrode was about 10�13 mole.
The immobilization of single-stranded DNA (ss-DNA) on
the gold electrodes and the subsequent hybridization to form
ds-DNA can be characterized by faradic electrochemical
impedance spectroscopy (EIS).22,23 The impedance spectra
consist of a semicircular portion at high frequencies and a
linear part at low frequencies. The semicircle relates to
an electron transfer-limited process, while the linear part
corresponds to a diffusion-limited process. The change in the
diameter of the semicircle reflects the change in the interfacial
charge-transfer resistance (Rct). The change of the Rct value
reflects the extent of the immobilization and hybridization of
DNA on the gold electrode surface. Therefore, we can know
the properties of DNA immobilization and hybridization
clearly by the EIS measurement.
Optimization of the DNA self-assembly process is described
in the ESI.w Fig. 2 shows Nyquist plots of [Fe(CN)6]3�/4� at
the bare (a), ss-DNA modified (b), and ds-DNA modified gold
electrodes (c). For the bare Au electrode, the value of Rct was
about 78 O, displaying a very small semicircular domain. After
immobilization of DNAzyme, the value of Rct increased from
78 O to 246 O. The negatively charged phosphate backbone of
the DNA immobilized on the bare Au electrode prevented the
negatively charged redox probe [Fe(CN)6]3�/4� from reaching
the gold electrode, thus inhibiting interfacial charge transfer,
resulting in a larger Rct value than that of the bare gold
electrode.24 When the DNAzyme was hybridized with the
target DNA substrate strand on the electrode surface, the
Rct was enhanced to a much larger value (476 O).After hybridization, the negative charge on the gold electrode
surface will again increase and thereby prevent [Fe(CN)6]3�/4�
from reaching the gold electrode more effectively, thus
raising the Rct value. Therefore, the immobilization and the
hybridization of DNA are clearly shown to happen on the
bare gold electrode according to the change of the Rct value
by EIS.
When Pb2+ is introduced into the sensing system, the
substrate strand hybridized to the DNAzyme is broken into
two pieces, and TBR-NHS is released from the electrode
surface, which causes a decrease in the ECL intensity. It is
clear that the Pb2+ concentration can influence the amount of
TBR-NHS ester bound with the DNA on the modified
electrode. Fig. 3(A) shows ECL intensities from the modified
electrodes in the presence of different Pb2+ concentrations in
TAE solution (pH = 8.2) containing 10�5 mol l�1 TPA. The
ECL intensity is found to decrease with increasing Pb2+
concentration. Fig. 3(B) shows the relationship between
concentration of Pb2+ and ECL intensity. The ECL intensity
decreases linearly with Pb2+ concentration in the range
of 2.5 � 10�10 to 1.0 � 10�9 mol l�1. The regression
equation is
I/a.u. = �15.76CPb/(10�10 mol l�1) + 198.6, R = �0.9922.
where I is the ECL intensity, CPb is the Pb2+ concentration
and R is the regression coefficient. The detection limit for Pb2+
is 1.1 � 10�11 mol l�1 (defined as S/N = 3), which is lower
Fig. 2 Nyquist plots corresponding to the different electrodes.
(a) Bare gold electrode; (b) ss-DNA modified gold electrode and
(c) ds-DNA modified gold electrode. The data were recorded in the
presence of 5.0 mmol l�1 [Fe(CN)6]3�/4�, containing 0.1 mol l�1 KCl,
upon application of a biasing potential of 0.218 V, and a 5 mV
alternating voltage in the frequency range of 1–10 000 Hz.
Fig. 3 (A) ECL intensity curves from the modified ECL sensors with
different Pb2+ concentrations under CV scanning. (a) 0; (b) 2.5 �10�10; (c) 5.0� 10�10; (d) 7.5� 10�10; (e) 1.0 � 10�9 mol l�1 in 10 mM
TAE (pH 8.2) containing 10�5 mol l�1 TPA at the scan rate of
50 mV s�1, potential range: 0.8–1.6 V; (B) the calibration curves.
This journal is �c The Royal Society of Chemistry 2009 Chem. Commun., 2009, 6050–6052 | 6051
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than those of fluorescent,7 electrical12 and colorimetric25,26
biosensors for Pb2+.
The DNAzyme-based sensor is clearly sensitive to its
target ion. We also studied the specificity of the ECL sensor
by making measurements using several other divalent metal
ions. Fig. 4 shows the changes in the ECL intensity for
DNAzyme-modified gold electrodes after reaction with
0.5 nmol l�1 Pb2+, Ba2+, Cu2+, Ni2+, Mn2+, Zn2+ and
when using a blank buffer solution. Apart from Pb2+, the
reduction in the ECL intensity is very small for all the divalent
metal ions, with only Ba2+ causing a little interference.
However, in the presence of Pb2+, the reduction of the ECL
intensity is obvious. The response to lead ions is easily
distinguishable and therefore this ECL biosensor has a good
selectivity for discriminating Pb2+ from other contaminating
divalent ions.
In summary, an ECL sensor for the detection of Pb2+ based
on DNAzyme as a recognition element using Ru(bpy)32+ for
ECL signal readout has been designed. The sensor exhibits
excellent sensitivity and selectivity. The limit of detection is as
low as 0.1 nmol l�1, which is better than those of fluorescent,
colorimetric and electrical biosensors for Pb2+ detection.
The main advantages of the present sensor come from the
combination of the selectivity of DNAzyme and the sensitivity
of ECL, which may provide a platform for the fabrication
of ECL sensors for analysis of many small molecules or
metal ions. For example, DNAzymes specific for Cu2+,
Zn2+, Co2+ and Hg2+ have also been obtained. Hence,
one can use the same signal discrimination method to design
ECL sensors to detect and quantify many metal ions
conveniently.
This project was financially supported by the National
Basic Research Program of China (No. 2010CB732403), the
National Nature Sciences Funding of China (20735002, 20877019)
and the Special Foundation for Young Scientists of Fujian
Province, China (2008F3057).
Notes and references
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Fig. 4 ECL intensity changes for modified gold electrodes after
reaction with various divalent metal ions (all at 0.5 nmol l�1).
6052 | Chem. Commun., 2009, 6050–6052 This journal is �c The Royal Society of Chemistry 2009
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