Yiting Zheng1, Qingxuan Li1, Chenfei Wang2, Ming Su1. 1. Department of Chemical Engineering, Northeastern University, Boston, Massachusetts 02115, United States. 2. Wenzhou Institute, University of Chinese Academy of Sciences, Wenzhou, Zhejiang 325001, China.
Abstract
Highly sensitive detection of lead ions in water is of importance. This paper reports a new method to enhance the sensitivity of fluorescence detection of aqueous lead ions by exploiting the large volume reduction of hydrogels upon dehydration. Rhodamine-derived prefluorescent probes with high selectivity to lead ions are grafted on a carboxylated agarose hydrogel. Upon binding low-concentration lead ions, fluorescence emission is turned on. The dehydration of the hydrogel leads to a size reduction of over 40 times and an enhancement of fluorescence of 10 times at a lead-ion concentration of 10-7 M, allowing fluorescence detection with naked eyes. Given its low cost, easy operation, and high sensitivity, the volume reduction hydrogel can be used to detect lead ions in drinking water.
Highly sensitive detection of lead ions in water is of importance. This paper reports a new method to enhance the sensitivity of fluorescence detection of aqueous lead ions by exploiting the large volume reduction of hydrogels upon dehydration. Rhodamine-derived prefluorescent probes with high selectivity to lead ions are grafted on a carboxylated agarose hydrogel. Upon binding low-concentration lead ions, fluorescence emission is turned on. The dehydration of the hydrogel leads to a size reduction of over 40 times and an enhancement of fluorescence of 10 times at a lead-ion concentration of 10-7 M, allowing fluorescence detection with naked eyes. Given its low cost, easy operation, and high sensitivity, the volume reduction hydrogel can be used to detect lead ions in drinking water.
Lead ion is a devastating
environmental toxin.[1,2] Analytical
methods to detect aqueous lead ions include atomic absorption spectrometry,
inductively coupled plasma mass spectrometry, and optical emission
spectrometry,[3−6] but these methods are expensive and require trained personnel to
operate them. Fluorescent methods are often used to detect lead ions
in aqueous and organic solutions due to their operational readiness.[7−11] However, existing fluorescent probes can optically detect lead ions
at a sufficiently high concentration (>10–5 M)
because
of their low sensitivity. In the case of monolayer-based detection,
an even higher concentration of fluorescent probes (>10–4 M) is needed,[12,13] which is much higher than the
national standard for lead levels in drinking water.The low
sensitivity in fluorescent detection is because of low
concentration of metal ions in a given volume of optical excitation.
Preconcentration such as extraction can be used to enrich low-concentration
metal ions, but it needs more sample and extra operation steps and
may lead to contamination.[14−18] If the probes can be enriched after binding to metal ions, the sensitivity
can be enhanced without altering optical illumination and fluorescent
detectors.[19] One way of increasing local
concentration of fluorescent probes is to take advantage of size-changeable
hydrogels, whose volume can be reduced hundreds or even thousands
of times once dehydrated.[20,21] The idea of volume
increase of hydrogels has been used to locate and image proteins,
while it has not been used to enhance metal ion detection when the
volume of hydrogel decreases. Agarose gel shrinks more significantly
after dehydration than other hydrogels such as polyacrylamide gel
and gelatin,[22−24] while agarose lacks active moieties (i.e., amine,
carboxyl, or thiol groups) and cannot be modified directly.[25] Agarose can be activated to form carboxylated
agarose (CA) by oxidizing its primary alcohol groups, and CA can form
a stable hydrogel at room temperature.[26−29]This article describes
a new method to detect aqueous lead ions
at low concentrations with turn-on fluorescence on a size-shrinkable
hydrogel (Figure ).
A prefluorescent molecule will be immobilized on the hydrogel.[30,31] Once selective binding to lead ions occurs, the fluorescent signal
will be turned on. By shrinking the volume of the hydrogel where fluorescence
probes are chemically linked, the sensitivity of detection will be
enhanced, indicating that the fluorescent quench at a high fluorophore
concentration does not play a significant role. The prefluorescent
probe used here is a derivative of rhodamine, which is grafted onto
the CA backbone through an amine moiety. Once they bind to target
metal ions, the molecules undergo a structural change from a spirocyclic
lactam to an open-ring amide,[32,33] resulting in pink fluorescence
emission. The agarose hydrogel shrinks upon dehydration, and the density
of fluorescent probes increases in the gel, causing fluorescence signals
to be enhanced.
Figure 1
Scheme of enhanced turn-on fluorescence detection of lead
ions
with a dehydrating hydrogel.
Scheme of enhanced turn-on fluorescence detection of lead
ions
with a dehydrating hydrogel.
Experimental Section
Chemicals and Materials
Agarose powder
was obtained from IBI scientific. Rhodamine 6G (99%) was obtained
from Acros Organics. Lead perchlorate trihydrate [crystalline, Pb(ClO4)2], acetonitrile (99%), tris(2-aminoethyl)amine
(97%), dichloromethane (CH2Cl2), methanol (>99.8%),
and perfluorooctyltrichlorosilane (PFTOS, 97%) were obtained from
Alfa Aesar. Tetramethyl-1-piperidinyloxy (98%, TEMPO), sodium bromide
(>99.0%, NaBr), sodium hypochlorite solution (10–15%, NaClO),
anhydroussodium sulfate (NaSO4), N-(3-dimethylaminopropyl)-N′-ethylcarbodiimide (>97%, EDC), and sodium hydroxide
(NaOH) were obtained from Sigma. Polydimethylsiloxane (PDMS) was obtained
from Corning. Phosphate-buffered saline (PBS) was obtained from VWR.
Agarose Carboxylation
Agarose was
treated with a TEMPO–NaBr–NaClO system to oxidize primary
alcohol groups to CA as follows: 1 g of agarose powder was dissolved
in 80 mL of water at 90 °C. After adjusting the pH to 11 with
1 M aqueous NaOH, the solution was cooled down to room temperature
with stirring, and 22 mL of an aqueous solution containing 0.02 g
of TEMPO, 0.3 g of NaBr, and 2 mL of NaClO was added dropwise into
the agarose solution, and the pH of the solution was maintained at
10–11 by adding 1 M aqueous NaOH. The oxidation reaction was
completed in l.5 h. The solution was precipitated by adding a mixture
of 200 mL of isopropyl alcohol and 20 mL of acetone. The precipitate
was washed twice with ethanol, and the oxidized agarose was dialyzed
for 48 h and lyophilized to remove the solvent.
Grafting Turn-On Fluorescent Probes on Oxidized
Agarose
A rhodamine-based turn-on prefluorescent probe was
prepared according to the literature.[13] A total of 80 mg of oxidized agarose was dissolved in 10 mL of PBS,
followed by adding 40 mg of EDC to activate carboxyl groups at 80
°C for 1 h. The modified agarose was mixed with 20 mg of raw
agarose to form a hydrogel, which was immersed in deionized water
overnight. To graft the turn-on probe, the rinsed hydrogel was mixed
with 40 μL of 2 mg/mL turn-on fluorescent probe in acetonitrile
at 80 °C. After reaction for 1 h, the agarose was rinsed in a
mixed acetonitrile and water solution (volume ratio of 20:100) 3 times,
followed by centrifugation and evaporation.
Templated
Hydrogel Formation
In order
to generate hydrogels with defined geometry, a bottomless well made
of elastic PDMS was fabricated by using a polyacrylic well (with desired
shape and dimension) as the mold. The bottomless well was firmly bonded
to plasma-treated glass substrates. The fluorescent probe-immobilized
hydrogel at a mass ratio of agarose and water of 1:99 was then injected
into the PDMS template and taken out by separating the PDMS template
and glass substrate after gelation.
Metal
Ion Detection
Aqueous solutions
of a variety of metal ions were prepared by dissolving corresponding
salts in water with concentrations ranging from 10–1 to 10–7 M. The templated hydrogel was immersed
in the solution of each metal ion at 60 °C for 30 min, followed
by rinsing with acetonitrile–water (1:10). The hydrogel was
dehydrated on a PFTOS-modified hydrophobic glass substrate and dried
at 70 °C for 30 min.The fluorescent images of hydrogels
after catching metal ions were taken using an Olympus BX51 fluorescence
microscope. The fluorescence intensity at each pixel of an image was
derived by using ImageJ software. The zeta potential change of the
hydrogel before and after modification was measured with a NANO ZS
ZEN3600 zeta potential analyzer (Malvern Instruments). Fourier transform
infrared (FTIR) spectra of hydrogels were collected with a spectrometer
(Bruker Vertex 70) combined with a Hyperion 1000 microscope.
Results and Discussion
Figure A shows
the procedures of modifying agarose, where the primary hydroxyl groups
of agarose are oxidized to carboxyl groups in CA, followed by grafting
prefluorescent probes through the carboxyl–amine reaction.
The prefluorescent probes do not produce fluorescence because carbon–nitrogen
bonds destroy the conjugation structure in rhodamine and prevent it
from fluorescence emission. Metal ions can bind to the amine group
since the lone pair electrons of an amine group have a strong affinity
to the outer shell of the metal ion. Once bound to a target cation,
the molecule will undergo a structural change from a spirocyclic lactam
to an open-ring amide, which results in fluorescence in pink. The
zeta potential of the aqueous solution of pristine agarose is nearly
neutral (−2 mV), and oxidized agarose is negatively charged
(−16.8 mV) due to formation of carboxyls. FTIR spectra indicate
the vibrational peaks of carboxyl groups of oxidized agarose at the
wavenumbers of 1400 and 1600 cm–1 (Figure B). The zeta potential increases
slightly (−9 mV) after immobilization of prefluorescent probes
due to attachment of amines. The FTIR spectrum shows the vibrational
peak of benzene on rhodamine at 1500 and 2900 cm–1, which confirms successful immobilization of prefluorescent probes.
Figure 2
Chemical
formula of agarose and modified agaroses (A). FTIR spectra
of agarose (B lower), CA (B middle), and fluorescent probe-immobilized
agarose (B upper).
Chemical
formula of agarose and modified agaroses (A). FTIR spectra
of agarose (B lower), CA (B middle), and fluorescent probe-immobilized
agarose (B upper).Figure A shows
the digital images of metal ion solutions without (upper) and with
(middle) UV (365 nm) excitation, as well as with prefluorescent probes
and UV light (lower). Each cuvette contains one type of 10–2 M metal ion including iron, copper, calcium, cobalt, and lead (left
to right). The fluorescent probe is found to be highly selective to
lead ions. Fluorescent spectroscopy (Figure B) shows that the maximum emission of the
probe–lead pair is at 530 nm. The fluorescent intensity of
the probe–lead pair is 10 times stronger than those of pairs
formed by the probe and other ions. Figure C shows the time-dependent fluorescent intensity
of the prefluorescent probe after mixing with lead ions (10–3 M, pH of 7). The fluorescent intensity of the mixture increases
with time, and reaches a plateau after 15 min. Figure D shows that the pH of the solution affects
the fluorescent intensity. The fluorescent intensity is negligible
when the pH is greater than 10 and when the lead ion is precipitated
as lead oxide in an alkaline solvent, while the fluorescent probe
is not selective to lead ions in a solution with a pH below 4. Therefore,
the operational pH range of the fluorescent probe is between 4 and
10. In addition, the shrinking ability of the CA hydrogel is tested
by volume measurement. Figure A shows the dry volume of CA as a function of agarose mass
ratio in the original hydrogel (volume of 15 mL), where 97.5% volume
reduction has been achieved when 1% by weight of agarose hydrogel
is used. This volume reduction could enrich molecules in dry agarose
to a 40-times higher density theoretically.
Figure 3
Digital images of metal
ion solutions under different conditions:
with the prefluorescence probe under natural light (A upper), without
the prefluorescence probe but under UV excitation (A middle), and
with the prefluorescence probe and under UV excitation (A lower);
fluorescent spectra (B), time-dependent intensity (C), and pH-dependent
intensity (D) of 10–4 M metal ion solutions containing
the prefluorescence probe.
Figure 4
Dehydrated
volume of a 15 mL hydrogel with different amounts of
agarose (A); optical images of the hydrogel before (B left) and after
(B right) dehydration under UV light; fluorescence micrographs of
the dehydrated hydrogel with physically absorbed rhodamine 6G (C left)
and with immobilized fluorescent probe (C right); the relationship
between fluorescent intensity and lead ion concentrations (D).
Digital images of metal
ion solutions under different conditions:
with the prefluorescence probe under natural light (A upper), without
the prefluorescence probe but under UV excitation (A middle), and
with the prefluorescence probe and under UV excitation (A lower);
fluorescent spectra (B), time-dependent intensity (C), and pH-dependent
intensity (D) of 10–4 M metal ion solutions containing
the prefluorescence probe.Dehydrated
volume of a 15 mL hydrogel with different amounts of
agarose (A); optical images of the hydrogel before (B left) and after
(B right) dehydration under UV light; fluorescence micrographs of
the dehydrated hydrogel with physically absorbed rhodamine 6G (C left)
and with immobilized fluorescent probe (C right); the relationship
between fluorescent intensity and lead ion concentrations (D).Figure B shows
that fluorescence emission from wet agarose treated with 10–4 M lead ions is hard to see under UV light, while it is obvious in
dried agarose. Figure C (right) shows the fluorescence from the dried hydrogel observed
with microscopy, where the fluorescence intensity is uniform across
the whole gel. In contrast, the fluorescence of the hydrogel with
physically adsorbed rhodamine shows uneven distribution after drying
(Figure C left), suggesting
that chemically immobilized fluorescence molecules undergo the same
volume change as the hydrogel itself and do not aggregate during drying. Figure D shows that a linear
relation exists between fluorescence intensity and the concentration
of fluorescence probes in the hydrogel, where an excess amount of
lead ions is added to ensure all prefluorescent probes are lighted.
Therefore, the fluorescence intensity should be exponential to the
level of lead ions.Figure A shows
the fluorescence images of lighted hydrogels with different loads
of lead ions before (upper) and after drying (middle) taken at the
same UV excitation and exposure time (100 ms), confirming that the
hydrogel dehydration enhances fluorescence. Meanwhile, the cubic hydrogel
dries to achieve a rectangular shape because water evaporation occurs
preferentially at the sides of the rectangle (due to large contact
areas with air), which produces a mass transfer of the wet hydrogel
from the center to the edge (Figure B). The detection sensitivity to lead ions is enhanced
to 10–7 M by comparing the fluorescence contrasts
of the edge of the dry hydrogel and background. The fluorescence intensity
at the edge of a dried rectangular-shaped gel is derived by ImageJ.
The intensity of fluorescence depends on the amount of the fluorescence
probe and geometry of the dried hydrogel. Figure B shows an exponential dependence of the
fluorescence intensity on the lead ion level (from 10–7 to 10–3 M), where red and black bars are fluorescent
intensities of hydrogels before and after dehydration, respectively.
The enhancement ranges from 3 times at low concentrations to more
than 10 times at high concentrations, compared to those of wet hydrogels. Figure C shows the fluorescence
intensity of the hydrogel in a vertical direction as a function of
thickness during the dehydration process, where the hydrogel is confined
inside a Petri dish to allow evaporation only through the top surface.
The fluorescent intensity increases by 20% during dehydration, which
is much smaller than the lateral direction. The relatively small increase
in fluorescence is due to the fact that the number of fluorescence
probes in the vertical direction does not increase much after dehydration.
Therefore, the fluorescence intensity should be exponential to the
level of lead ions. The US Environmental Protection Agency regulates
that the lead ions in drinking water should be below 10–7 M; thus, this method allows visual examination against lead ions
in drinking water.
Figure 5
Fluorescence micrographs of the hydrogel (A upper), after
dehydration
(A middle), and selected regions for intensity analysis (A lower)
(exposure time: 100 ms); fluorescent intensity as a function of lead
ion concentration before (black) and after (red) dehydration (B);
fluorescent intensity as a function of hydrogel thickness at different
lead ion concentrations with vertical dehydration (C).
Fluorescence micrographs of the hydrogel (A upper), after
dehydration
(A middle), and selected regions for intensity analysis (A lower)
(exposure time: 100 ms); fluorescent intensity as a function of lead
ion concentration before (black) and after (red) dehydration (B);
fluorescent intensity as a function of hydrogel thickness at different
lead ion concentrations with vertical dehydration (C).
Conclusions
The volume reduction of hydrogels
upon dehydration is used to enhance
the sensitivity of turn-on fluorescence detection of lead ions in
water. The rhodamine-derived fluorescent probes grafted on CA hydrogel
show excellent selectivity to lead ions and superior turn-on fluorescence
upon binding lead ions. The dehydration of hydrogel leads to a volume
reduction of more than 40 times and can effectively increase fluorescence
emission to 10 times higher after capturing lead ions at a concentration
of 10–7 M. The enhancement is at such a degree that
the turn-on fluorescence upon lead ion binding can be easily seen
with naked eyes. Given its low cost, straightforwardness, easy operation,
and high sensitivity, this volume-changing hydrogel can be used to
detect lead ions in drinking water.
Authors: Irina Yu Goryacheva; Sergei N Shtykov; Alexander S Loginov; Irina V Panteleeva Journal: Anal Bioanal Chem Date: 2005-07-02 Impact factor: 4.142