A Biosensor to Measure Fungicide Iprovalicarb Residues in Agricultural Products

A Biosensor to Measure Fungicide Iprovalicarb Residues in Agricultural Products

EAEF 1(2) : 63-67, 2008 Invited Paper A Biosensor to Measure Fungicide Iprovalicarb Residues in Agricultural Products* Han Keun CHO *1, Kee Sung KYU...

250KB Sizes 0 Downloads 36 Views

EAEF 1(2) : 63-67, 2008

Invited Paper

A Biosensor to Measure Fungicide Iprovalicarb Residues in Agricultural Products* Han Keun CHO *1, Kee Sung KYUNG*2 Abstract Using an enzyme-linked immunosorbent assay (ELISA), a biosensor was developed to rapidly measure fungicide iprovalicarb residues in agricultural products. The biosensor was designed to include micro-pumps and solenoid valves for fluid transport, a spectrophotometer cuvet›Œ as a reaction chamber, a photodiode with a light-emitting diode for optical density measurement, and a control microcomputer to implement assay. The rate of change in optical density of the cuvette was read as final signal output.

Micro-pumps were evaluated to investigate their

delivery capability. The maximum error and the coefficient of variation were found to be 4.3% and 4.6%, respectively. To predict the concentration of the iprovalicarb residue in agricultural products, a linear calibration model was obtained with r-square values of 0.992 for potato and 0.985 for onion.

In validation test for the samples

of potatoes and onions against the high performance liquid chromatography (HPLC), very high correlation values were obtained as 0.996 and 0.993, respectively. Using the cuvette immobilized with antigen, it took 21-minutes for the biosensor to complete the measuring process of the iprovalicarb residues . The measurement assay was successfully automated with an adequate sensitivity level to measure the government limits for iprovalicarb residues. [Keywords] biosensor, elisa, antibody, antigen, iprovalicarb, fungicide residues

I

Introduction

The fungicide iprovalicarb is extensively used in Korea for the control of anthracnose, downy mildew and black shank in many crops such as potato, onion, cucumber, tomato, grape, and watermelon. Although its half-life is not very long, residue problem may arise in agriculturalG products and environment. Iprovalicarb, isopropyl 2-methyl-1-[(1-p-tolylethyl) carba moyl]-(S)-propylcarbamate, belongs to the new amino acid amidocarbamate class of compounds and is a protective, curative, and eradicative systemic fungicide introduced by Bayer AG in 1999. The product is a mixture of (SS)-and (SR)-diastereoisomers (Lee et al., 2004).

iprovalicarb residues in agricultural products. A biosensor in general can be defined as an analytical device consisting of a biological sensing element in close association with a physical transducer.

The biological recognition element performs the

molecular recognition function responsible to specific sensing of an analyte of interest and then the physical transducer converts the recognition event into a measurable optical or electrical signal. The objective of this research was to (1) design an automated biosensorGto implement an enzyme immunoassay for rapid detection of the fungicide iprovalicarb residues in vegetables, and (2) calibrate the biosensor and evaluate its measurement performance.

A simple, sensitive, and cost-effective ELISA was developed by Lee et al. (2004) for the detection of iprovalicarb residue in agricultural and environment samples. Automated biosensor systems are needed at both the producer and wholesaler levels to indicate the presence of the

IIG Materials and Methods 1. Chemicals Iprovalicarb and p-methylphenylamine, of analytical grade were gifts from BayerG AG.

BovinG serum albumin (BSA),

* Partly presented at the Conference of ISMAB in May 2008 *1 KSAM Member, Corresponding author, Professor, Department of Biosystems Engineering, Chungbuk National University, Cheongju, 361-763, Rep. of Korea; phone: +82-43-261-2585, fax: +82-43-271-4413; [email protected] *2 Assistant Professor, Department of Agricultural Chemisitry, Chungbuk National University, Cheongju, 361-763, Rep. of Korea.

64

Engineering in Agriculture, Environment and Food Vol. 1, No. 2 (2008)

obtained from Sigma Chemical Co. (St. Louis, MO). A

solenoid activated pumps, each rated at 50 LG per stroke (LPLAG1220050L, The Lee Co., Westbrook, Ct.). Two-way

polyclonal antibody produced against a hapten conjugated and

normally-closed valves were used for priming the lines

goat anti-rabitG (IgG) and peroxidaseG conjugate, were all

a coating antigen were provided by Lee et al. (2004). Buffer

(LFFAG 1201710H and LFFAG 1201410H, The Lee Co.). A

solutions were normal strength phosphate-buffered saline (1

separate pump and lines were used for the labeled

โPBS, 0.001 M KH2PO4, pH7.5), PBST(1โPBS containing

iprovalicarbG conjugate to minimize contamination of the

0.05% Tween 20), carbonate buffer(pH 9.6), and 0.05 M

reagent pump, manifold, and priming valve with peroxidase.

borate buffer (pH 8). Each buffer was prepared according to

The mix pump was used to provide recirculation of the

the method used in Lee et al. (2004).

reaction chamber to enhance the binding process and the air pump was used to dry out the tubes. The substrate, conjugate, mix, and supply lines to the

2. Assay development The previous research developed an enzyme immunoassay for

reaction chamber were made from 1.6 mm inner diameter

iprovalicarb suitable for use in a sensor by modifying the

VitonG tubing (06434-01, Cole-ParmerG Instrument Corp.,

results of Cho et al. (2006). The dilution of coating antigen

Vernon Hills, IL.), with the remaining lines TygonG tubing

and both primary and secondary antibodies were increased to

(14-169-1B, Fisher Scientific, Pittsburgh, Pa) of the same

improve the competition and incubation time was reduced to

inner diameter. Stainless steel tubes with an inner diameterGof

save test time.

1.1 mm (HTX-17, Small Parts Inc., Miami Lakes, CA.) were

The modified procedure for iprovalicarb

ELISAGis summarized in Table 1.

inserted in a TeflonGspacer cap and used to inject the reagents and drain the chamber. Absorbance of the substrate was measured by positioning a 645 nmGlight-emitting diode (LED,

Table 1 Protocol for the ELISA used in the biosensor (Cho et al.,

HLMP-4101, Hewlett Packard, San Jose, CA) on one side of the reaction chamber and a large-area photodiodeG(BPXG61,

2006) Immobilization of Antigen (By hand) 1. Immobilize antigen on cuvette (1 mL, 1 Ǵg/mL, 12 hr, 4͠) 2. Washing cuvette (1˜PBS + 0.05% Tween20, 5 times) 3. Blocking cuvette (2 mL, 1˜PBS + 3% skim milk, 1 hr, 37͠) 4. Washing cuvette (1˜PBS + 0.05% Tween20, 5 times) Binding (By the biosensor) 5. Add 500 ǴL of sample (5000, 200, 8, 0.32, 0.0128 ng/mL) 6. Add 500 ǴL of the 1st-antibody (1:4,000) 7. Incubate for 5 or 3 minutes at 24͠ 8. Washing cuvette (1˜PBS + 0.05% Tween20, 5 times) 9. Add 1 mL of the 2nd-antibody (1:1,000) 10. Incubate for 5 or 3 minutes at 24͠

Siemens Components, Inc., Cupertino, CA) on the other side. Light from the LED was collimated with a simple peep-hole configuration (DelwichGet al., 2001). Light current from the photodiodeGwas fed to the input of a photovoltaic amplifier with a gain of 104G V/A.

frequency noise was then removed with a 4th order ButterworthGlow-pass filter (fc=10 Hz). An inverter with a fixed gain of 10 and adjustable offset was used in the final stage, with output voltage proportional to the intensity of light transmitted through the substrate. Relative optical density was calculated based on the output at the start of substrate development.

11. Washing cuvette (1˜PBS + 0.05% Tween20, 5 times)

Air

Development (By the biosensor)

Wash Sample 1st Ab Substrate solution

12. Add 1 mL of substrate buffer

Priming valve (3-way)

(citrate buffer, 0.6% TMB, 1% H2O2 ) 13. Incubate for 5 minutes at 24͠ 14. Read optical density

Low

Reagent valves (2-way)

Manifold

Reagent pump

Drain pump

Waste nd

2 Antibody pump

Mix pump Stainless steel tubes

3. Sensor design A schematic of the fluid handling system is shown in figure 1. A standard quartz cuvetteG(TypeG5 H, NSGGPrecision Cells,

LED

Photodiode 2nd Antibody Reaction chamber

Inc., Farmingdale, N.Y.) was used as the reaction chamber to minimize optical and chemical interfaces. Reagents were pumped into and out of the reaction chamber with four

Fig. 1

Schematic of the biosensor fluidics

65

CHO, KYUNG : A Biosensor to Detect Fungicide Iprovalicarb in Vegetebles 4. Prototype of the biosensor A prototype of the biosensor developed is shown in Figure

Table 2 Control sequence for the biosensor

2. Two control circuit boards are located in the upper side of

Binding cycle

the sensor box, a larger board (1) in rear includes a

‫ ك‬Sample valve (500 ǴL), Reagent pump (10 strokes)

microcomputer, signal processing and control part, a smaller board (2) in front includes a LCD (liquid cristal display) to

‫ ك‬1st antibody valve (500 ǴL), Reagent pump (10 strokes)

display the final concentration of the sample and five control

‫ ك‬Mix pump (28 strokes)

switches. Six solenoid valves (3) and four micro-pumps (4)

‫ ك‬Incubate 5 or 3 min. (24͠)

are located in middle part of the sensor box. Four chemical

Washing cycle ˜ 5

vessels (5) are located at the left lower side and a black

‫ ك‬Drain cuvet

reaction chamber (6) with absorbance measuring unit is

‫ ك‬Washing valve (1.2 mL), Reagent pump (26 strokes)

located at the right lower side of the sensor box.

‫ ك‬Mix pump (28 strokes) Labeling cycle ‫ ك‬2nd antibody pump (19 strokes) ‫ ك‬Incubate 5 or 3 min. (24͠) Washing cycle ˜ 5 Development cycle ‫ ك‬Substrate valve (1 mL), Reagent pump (17 strokes) ‫ ك‬Incubate 5 min. (24͠) ‫ ك‬Calculate OD rate (10 s) Cleaning cycle ‫ ك‬Clear sample valve G

‫ ك‬Clear substrate valve ‫ ك‬Add washing solution

Fig. 2

Picture of the biosensor prototype 6. Evaluation of the biosensor The performance of fluid transfer by pumps and valves was

5. Control of the biosensor Figure 3 shows the control logic diagram of the biosensor.

investigated using distilled water and an electronic weigh

A microcomputer (AVR, ATmega 8535, ATMEL) was used

scale. Each transfer process was replicated 10 times. The

to sequence the pumps and valves with Darlington driver, and

calibration curve of the biosensor was obtained in two ways:

read the sensor output with A/D conversion. Finally the

the general calibration curve with iprovalicarb samples in

concentration of the iprovalicarb was displayed as voltage

PBS buffer which concentration is known and the specific

output on the LCD. The detail control sequence of the

calibration curve according to the agricultural products such

biosensor is summarized in Table 2.

as

cucumbers

and

potatoes.

Finally

the

biosensor

measurements were compared against HPLC (HP 1100 series, Agilent Technologies Korea, Young-In Scientific, Korea) Air

Darlington driver for valves

Photodiode Photodiode

Wash Sample

1st Antibody

Signal Signal processor processor

Microcontroller

Substrate

Priming (3-way)

LED LED

LCD LCD

Darlington driver for pumps

As the buffer standard samples, five levels of concentration prepared are 0.0128, 0.32, 8, 200, and 5000 ng/mL. The dilution ratios of antibody used are 1:2,000 for the 1st antibody and 1:500 for the 2nd antibody. The incubation time was varied from 15 minutes to 11 minutes. Onion and potato samples were used for evaluation of the

Reagent

biosensor.

Drain

sample has been described in more detail (Lee et al., 2004).

2nd Antibody Mixing

Fig. 3

results.

Control logic of the biosensor

The preparation procedure of extracting each

The potato samples were fortified with the stock solution of iprovalicarb dissolved in CH3CN to 1, 2, 3 ng/mL and the onion samples were fortified to 2, 4, 6 ng/mL.

66

Engineering in Agriculture, Environment and Food Vol. 1, No. 2 (2008)

III Results and Discussion

y

1. Chemical transfer performance The result of dispensed volume to a cuvette by

a b b 1  ( x / c) d

(1)

where y : Optical density

micro-pumps is shown in Table 3. In case of reagent pumps,

x : concentration (ng/mL) a : initial y value b : final y value

the error rates ranged from 0.7 to 2.1 %. The error rates of the 2nd antibody pump, mixing pump and drain pump are shown to be 4.3%, 1.6% and 3.3%, respectively. The coefficients

c : center d : power

of variation (CV) ranged from 0.1 to 4.6%. All pumps were found to be acceptable to transfer chemicals accurately. Table 3

Test results of dispensed volume to a cuvette

Table 4

by micro-pumps

calibration curve

Set

Meas’d

Error

CV

Incubation time, minutes

(mL)

(mL)

(%)

(%)

(Bind-label-development)

Sample

500.0

510.5

2.1

0.5

1st Ab

500.0

507.8

1.6

1.5

Substrate

1000.0

1019.2

1.9

0.3

Wash

1200.0

1208.2

0.7

0.3

Micro-pumps

Reagent

Parameter values of sigmoidal model for

nd

2 Ab

1000.0

1042.7

4.3

4.6

Mixing

1200.0

1219.6

1.6

1.6

Drain

1200.0

1239.8

3.3

0.1

Sigmoidal model parameters a

b

c

d

5-5-5

0.202 0.055 18.609 0.311

3-3-5

0.552 -0.349 68.477 0.069

3. Calibration with crops Results from calibrating the biosensor with known samples of potato and onion are plotted in Figure 5. The horizontal axis shows the concentration of the vegetable extract and the vertical axis shows the relative optical

2. Calibration with buffer solution In general, the similar magnitudes of optical density for the

density. The calibration equation was derived by solving

sensor were observed as compared with results obtained when

the regression result for the predicted concentration.

In the

performing the assay by hand.

Figure 4 shows the

concentration range tested from 0.0128 to 5000 ng/mL, the

calibration curve with standard sample solution of the

optical density showed a good linear correlation with

iprovalicarb for different incubation times. The horizontal

iprovalicarb concentration. The r-square values of the linear

axis shows the concentration of standard iprovalicarb solution

models are obtained as 0.985 and 0.988 for potato and onion,

and the vertical axis shows the relative optical density. The

respectively. The linear regression equations of both onion

r-square value of the sigmoide model is 0.999 and 0.997 for

and potato are shown in the plot.

each incubation time. The model equation is shown in Eq. (1) and those parameter values of sigmoid model are shown in Table 4. 0.28 Onion Potato

0.26 0.24

Incubation 5-5-5 min Incubation 3-3-5 min

0.20 0.18

Optical density

0.16 0.14

Optical density

0.22

0.22

y=0.206-0.032x

0.20

r-sq=0.985

0.18 0.16 0.14

y=0.189-0.025x

0.12

0.12

r-sq=0.988

0.10

0.10

0.08

0.08 0.01

0.06

0.1

1

10

100

1000

10000

Iprovalicarb concentration, ng/mL

0.04 0.01

0.1

1

10

100

1000

10000

Iprovalicarb concentration, ng/mL

Fig. 5

Sensor calibration results for onion and potato extracts

Fig. 4

Sensor calibration results for the incubation time

67

CHO, KYUNG : A Biosensor to Detect Fungicide Iprovalicarb in Vegetebles 4. Comparison of the biosensor with HPLC As illustrated in Figures 6 and 7, a good linear correlation is shown for the biosensor measurements at the iprovalicarb concentration tested with HPLC measurements.

As shown

in the figures the correlation coefficients were 0.996 and 0.993 for the potato and the onion, respectively.

These

results suggested that the fungicide iprovalicarb residue in potato and onion could be measured with developed biosensor in the comparable degree of HPLC accuracy.

V Summary and Conclusions A

biosensorG for

rapid

measurement

of

fungicide

iprovalicarbG residue was designed and constructed. An enzyme immunoassay developed by Lee et al. (2004) and modified by Cho et al. (2006) was automated.

This

biosensorGincludes a reaction chamber with absorbance sensor, micro fluidics, signal conditioner, and a microcomputer for control. Results from the calibration test showed that the iprovalicarbGresidues in potato and onion could be measured with the degree of accuracy as HPLC.

The sensitivity level

is also adequate to detect the government limits for iprovalicarb residues indicating that the measurement assay

3.5

Concentration by biosensor, ng/mL

y=1.148x-0.114 (r=0.996)

was successfully implemented.

3.0

This biosensor could

execute a measurement cycle in 21-minutes with the cuvette 2.5

immobilized.

2.0

References

1.5

Cho, H. K., K. S. Kyung and E. Y. Lee. 2006. Enzyme immunoassay

1.0

for rapid detection of the fungicide iprovalicarb residues. J. of

0.5

Biosystems Eng. 31(6):535-540. (In Korean) 0.0

Crowther, J. R. 2001. The ELISA Guidebook. Hummana Press, 0.0

0.5

1.0

1.5

2.0

2.5

3.0

3.5

Concentration by HPLC, ng/mL

Totowa, New Jersey. Delwiche, M. Tang, X. BonDurant, R. Munro, C. 2001. Improved Biosensor for measurement of Progesterone in Bovine milk. Trans. of the ASAE 44(6):1997-2002.

Fig. 6

Correlation of potato iprovalicarb residues measured by the biosensor and HPLC.

Lee, J. K., S. H. Park, O. S. Park, E. Y. Lee, Y. J. Kim and K. S. Kyung. 2004. Development of an ELISA for the detection of the residues of the fungicide iprovalicarb. J. Agric. Food Chem. 52: 6680-6686. (Accepted : 31. July. 2008)

y=1.039x-0.186 (r=0.993)

Concentration by biosensor, ng/mL

6

5

4

3

2

1

0 0

1

2

3

4

5

6

Concentration by HPLC, ng/mL

Fig. 7

Correlation of onion iprovalicarb residues measured by the biosensor and HPLC.