A Filter-based Surface Enhanced Raman Spectroscopic Assay for Rapid Detection of Chemical Contaminants

Podsumowanie

A procedure for fabrication and performing the filter-based surface enhanced Raman spectroscopic (SERS) assay for the detection of chemical contaminants (i.e., pesticide ferbam and antibiotic ampicillin) is presented.

Streszczenie

We demonstrate a method to fabricate highly sensitive surface-enhanced Raman spectroscopic (SERS) substrates using a filter syringe system that can be applied to the detection of various chemical contaminants. Silver nanoparticles (Ag NPs) are synthesized via reduction of silver nitrate by sodium citrate. Then the NPs are aggregated by sodium chloride to form nanoclusters that could be trapped in the pores of the filter membrane. A syringe is connected to the filter holder, with a filter membrane inside. By loading the nanoclusters into the syringe and passing through the membrane, the liquid goes through the membrane but not the nanoclusters, forming a SERS-active membrane. When testing the analyte, the liquid sample is loaded into the syringe and flowed through the Ag NPs coated membrane. The analyte binds and concentrates on the Ag NPs coated membrane. Then the membrane is detached from the filter holder, air dried and measured by a Raman instrument. Here we present the study of the volume effect of Ag NPs and sample on the detection sensitivity as well as the detection of 10 ppb ferbam and 1 ppm ampicillin using the developed assay.

Wprowadzenie

Surface enhanced Raman spectroscopy (SERS) is a technique combining Raman spectroscopy with nanotechnology. The intensity of Raman scattering of analytes at noble metallic nano-surfaces is greatly enhanced by the localized surface plasmon resonance.¹ Silver nanoparticles (Ag NPs) are by far the most widely used SERS substrates due to its high enhancement ability.² Up to now, various synthetic methods of Ag NPs have been developed.^3-6 Ag NPs can be used alone as effective SERS substrates, or combined with other materials and structures to enhance its sensitivity and/or functionality.^7-11

SERS techniques have demonstrated great capacity for detection of various trace amount contaminants in food and environmental samples.¹² Traditionally, there are two common ways for preparing a SERS sample: solution-based and substrate-based methods.¹³ The solution-based method uses NP colloids to mix with samples. Then the NP-analyte complex is collected using centrifugation, and deposited onto a solid support for Raman measurement after drying. The substrate-based method is usually applied by depositing several microliters of liquid sample onto the pre-fabricated solid substrate.¹⁴ However, neither of these two methods are effective and applicable for a large amount of sample volume. Several modifications of the SERS assays overcame the volume limits, such as the integration of a filter system^15-21 or the incorporation of a microfluidic device.^21-24 The modified SERS assays have shown great enhancement in sensitivity and feasibility for monitoring the chemical contaminants in large water samples.

Here we demonstrate the detailed protocol of fabrication and application of a syringe filter based SERS method to detect trace amount of pesticide ferbam and antibiotic ampicillin.

Protokół

1. Silver Nanoparticle Synthesis¹⁵

1. Dissolve 18 mg silver nitrate in 100 ml ultrapure water (18.2 ΩU) and vortex for 5 sec.
2. Dissolve 27 mg sodium citrate dihydrate in 1 ml water and vortex for 5 sec.
3. Transfer all of the prepared silver nitrate solution to a conical flask containing a stirring bar and put the flask on a magnetic hot plate. Heat the flask under vigorous stirring with a stirring speed of 700 rpm at ~350 °C (setting temperature on the plate).
4. When boiling, add all of the prepared sodium citrate solution to the conical flask immediately, and leave the solution to boil for an additional 25 min until the solution turns greenish brown, which indicates the formation of Ag NPs.
5. Remove the flask from the hot plate and put it on another magnetic plate (do not heat) and stir O/N at the same stirring speed at RT until the mixture reaches a stable state, with a constant color and transparency. Use a UV-vis spectrometer to determine the absorbance of the prepared Ag NPs if necessary.
6. Dilute the final mixture with ultrapure water to 100 ml.
7. Use a Zetasizer to measure the size of the Ag NPs if necessary according to manufacturer's protocol.
8. Transfer the Ag colloid to a sealed container and protect it from light with aluminum foil. The colloid can be stored in a refrigerator at 4-7 °C for 2 months if needed.

2. Fabrication of a SERS Active Filter Membrane

1. Dissolve 2.92 g sodium chloride (NaCl) in 100 ml water to make a 50 mM NaCl solution.
2. Add 1 ml of the 5 mM NaCl solution into 1 ml of the prepared Ag NPs and mix them on a nutating mixer for 10 min at 20 rpm. This step is to aggregate the Ag NPs into Ag nanoclusters.
3. Place a filter membrane (PVDF, 0.1 µm pore size) into a filter holder, which can be attached to a syringe. The smaller pore size membrane was found more effective than the larger pore size membrane (i.e., 0.22 µm) in trapping Ag nanoclusters and producing consistent signals.
4. Load 2 ml of the prepared Ag nanoclusters into the syringe for filtration. Attach the filter holder to the syringe and manually pass the entire volume of Ag nanoclusters through the membrane at the flow rate of 1 drop/sec. The membrane traps Ag nanoclusters, forming a SERS-active filter membrane.
5. Detach the filter membrane from the filter holder. Special caution is needed when holding the membrane on the outer rim using a pair of tweezers to ensure no damage to the membrane. Air dry for about 3 min and place membrane on a glass slide.
6. Raman detection of the SERS substrate
   1. Set the Raman instrument to a 780 nm wavelength laser with a laser power of 5 mW, exposure time of 1 sec and exposure number of 2. Set the microscopic objective to 10X. Make sure the objective on the software is set accordingly too.
   2. Place the glass slide with the membrane on top onto the platform of the Raman instrument and use the microscope to focus on the surface of the membrane.
   3. Randomly select 8-10 spots from the membrane surface and the instrument will collect them automatically in sequence. Open spectral data in manufacturer's software for analysis.

3. Application of the SERS Active Filter System to Detect Chemical Contaminants

1. Prepare a 10 ppb ferbam solution.
   Caution: Ferbam is highly volatile. Use precautions (respirator and goggles) when weighing the solid.
   1. Weigh 2 mg ferbam powder and dissolve it in 20 ml 50% acetonitrile (10 ml acetonitrile and 10 ml water) to make a stock solution (100 ppm). Vortex the flask for 30 sec.
   2. Take 1 ml of the 100 ppm ferbam solution in a test tube and add 9 ml 50% acetonitrile to make a 10 ppm solution. Vortex the tube for 5 sec.
   3. Take 1 ml of the 10 ppm solution in a test tube and add 9 ml 50% acetonitrile to make a 1 ppm solution. Vortex the tube for 5 sec.
   4. Take 1 ml of the 1 ppm solution in a test tube and add 9 ml 50% acetonitrile to make a 100 ppb solution. Vortex the tube for 5 sec.
   5. Take 1 ml of the 100 ppb solution in a test tube and add 9 ml 50% acetonitrile to make a 10 ppb solution. Vortex the tube for 5 sec.
2. Prepare a 1 ppm ampicillin solution.
   1. Weigh 10 mg ampicillin powder and dissolve it in 100 ml water to make a 100 ppm ampicillin solution. Vortex the flask for 30 sec.
   2. Take 1 ml of the 100 ppm solution in a test tube and add 9 ml water to make a 10 ppm ampicillin solution. Vortex the tube for 5 sec.
   3. Take 1 ml of the 10 ppm solution in a test tube and add 9 ml water to make a 1 ppm ampicillin solution. Vortex the tube for 5 sec.
3. Put the filter membrane back to the filter holder, with the NP coated side facing up.
4. Load 5 ml of one sample into a new syringe, and then attach it to the filter holder with a Ag coated membrane inside.
5. Manually pass the entire volume of sample through the membrane at the flow rate of 1 drop/sec. Target molecules can be adsorbed and concentrated onto the NPs coated on the filter membrane.
6. Detach filter membrane from the filter holder, air dry for about 3 min and measure the signals using the Raman instrument using the same method as described in step 2.6.
7. Repeat step 2.2 to 2.6 to prepare another Ag-coated membrane, and follow from step 3.3 for the detection of the other sample.

Wyniki

The major steps of this experiment were shown in the schematic diagram (Figure 1). Figure 2 demonstrated the importance to use the optimized volume of AgNPs in the membrane coating in order to reach the maximized sensitivity. 1 ml of Ag NPs provides the strongest signal when using ferbam, as compared to 0.5 ml (insufficient coating) or 2 ml (too much coating).

We were able to detect ferbam at 10...

Dyskusje

One of the critical steps in this protocol is the Ag NPs synthesis, where uniform Ag NPs are the key for consistent results. The heating time and the concentrations of precursors must be precisely controlled. The average size of this AgNPs preparation is 80 nm, which was measured by the Zetasizer (data not shown). Another critical step is the salt aggregation where the salt concentration and aggregation time must be precisely controlled. In addition, the choice of membrane is also critical as the membrane with a smaller ...

Materiały

Name	Company	Catalog Number	Comments
Ampicillin	Fisher Scientific	BP1760-5	N/A
Ferbam	Chem Service	N-11970-250MG	98+%
Silver nitrate	Sigma Aldrich	209139	99.0+%
Sodium citrate dehydrate	Sigma Aldrich	W302600	99+%
Sodium chloride	Sigma Aldrich	S7653	99.5+%
EMD Millipore Durapore PVDF Membrane Filters	Fisher Scientific	VVLP01300	0.10 µm Pore Size, hydrophilic
Polycarbonate Filter Holders	Cole-Parmer	EW-29550-40	13 mm diameter
Analog Vortex Mixer	Fisher Scientific	02-215-365	N/A
Nutating Mixers	Fisher Scientific	05-450-213	N/A
DXR Raman spectroscope	Thermo Scientific	IQLAADGABFFAHCMAPB	Laser power: 1 mW Exposure time: 5 sec