Determination of simazine in water samples by waveguide surface plasmon resonance
Determination of simazine in water samples by waveguide surface plasmon resonance
We assessed a new sensing device based on the monitoring of immunobinding reactions using Waveguide Surface Plasmon Resonance (WSPR) for the determination of simazine in water samples. Standard solutions between 0.1 and 1.0µg/l analysed in triplicate showed a mean within-day variability of 5%. Calibration curves for the same standards conducted on 5 consecutive days showed a 14% mean day-to-day variability. The detection limit calculated as 3 standard deviations below the mean blank value was 0.2µg/l. The upper limit of the working range calculated as a 90% decrease in the blank signal was 2.4µg/l. The cross-reactivity of atrazine and terbuthylazine was 61 and 67%, respectively. The recovery from spiked natural ground- and surface-water samples ranged from 55 to 153% for spikes ranging from 0.1 to 1.0µg/l. For the 11 surface- and 8 ground-water samples tested, the correlation coefficient between WSPR and HPLC/GC values was significant (p < 0.05) when the chromatography values were calculated as the weighted sum of simazine and atrazine, taking into account the predetermined cross-reactivity of the latter in the WSPR determination. The present system is therefore better suited for screening groups of pesticides than for the determination of a single molecule. An attempt at analysing a soil water sample proved unsuccessful due to interference probably resulting from strong non-selective polyanion-polycation binding to the transducer surface which includes a basic aminodextran. The total duration of one determination, 22 minutes, enables almost immediate measurements without any sample pretreatment other than 0.45µm filtration. No significant alteration of the sensor was observed after 200 determinations.
109-117
Mouvet, C.
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Harris, R.D.
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Maciag, C.
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Luff, B.J.
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Wilkinson, J.S.
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Piehler, J.
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Brecht, A.
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Gauglitz, G.
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Abuknesha, R.
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Ismail, G.
259c5b51-a414-4ffc-9a9a-5af3587b9498
February 1997
Mouvet, C.
03a5b635-3952-4136-bc6c-13441b230781
Harris, R.D.
e972b676-3335-44cd-b6e8-0dae17c550c3
Maciag, C.
138ab87a-7f39-45fa-af99-c7d83c846b82
Luff, B.J.
04d280ab-ae84-4715-9dad-6a1120050ccd
Wilkinson, J.S.
73483cf3-d9f2-4688-9b09-1c84257884ca
Piehler, J.
c7ccd012-3ad1-4b8a-aa0c-6244ab00630f
Brecht, A.
1b34ee2a-ada5-48ec-923a-f385835fbc83
Gauglitz, G.
119b102d-52db-4eba-81c0-0bdd5a16f1e7
Abuknesha, R.
5d66fe81-0e42-4c2f-af72-213ad83c731c
Ismail, G.
259c5b51-a414-4ffc-9a9a-5af3587b9498
Mouvet, C., Harris, R.D., Maciag, C., Luff, B.J., Wilkinson, J.S., Piehler, J., Brecht, A., Gauglitz, G., Abuknesha, R. and Ismail, G.
(1997)
Determination of simazine in water samples by waveguide surface plasmon resonance.
Analytica Chimica Acta, 338 (1-2), .
(doi:10.1016/S0003-2670(96)00443-6).
Abstract
We assessed a new sensing device based on the monitoring of immunobinding reactions using Waveguide Surface Plasmon Resonance (WSPR) for the determination of simazine in water samples. Standard solutions between 0.1 and 1.0µg/l analysed in triplicate showed a mean within-day variability of 5%. Calibration curves for the same standards conducted on 5 consecutive days showed a 14% mean day-to-day variability. The detection limit calculated as 3 standard deviations below the mean blank value was 0.2µg/l. The upper limit of the working range calculated as a 90% decrease in the blank signal was 2.4µg/l. The cross-reactivity of atrazine and terbuthylazine was 61 and 67%, respectively. The recovery from spiked natural ground- and surface-water samples ranged from 55 to 153% for spikes ranging from 0.1 to 1.0µg/l. For the 11 surface- and 8 ground-water samples tested, the correlation coefficient between WSPR and HPLC/GC values was significant (p < 0.05) when the chromatography values were calculated as the weighted sum of simazine and atrazine, taking into account the predetermined cross-reactivity of the latter in the WSPR determination. The present system is therefore better suited for screening groups of pesticides than for the determination of a single molecule. An attempt at analysing a soil water sample proved unsuccessful due to interference probably resulting from strong non-selective polyanion-polycation binding to the transducer surface which includes a basic aminodextran. The total duration of one determination, 22 minutes, enables almost immediate measurements without any sample pretreatment other than 0.45µm filtration. No significant alteration of the sensor was observed after 200 determinations.
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Published date: February 1997
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Local EPrints ID: 78101
URI: http://eprints.soton.ac.uk/id/eprint/78101
ISSN: 0003-2670
PURE UUID: cc426351-8af7-45af-86e7-b0e7aa20ab19
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Date deposited: 11 Mar 2010
Last modified: 14 Mar 2024 02:32
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Author:
C. Mouvet
Author:
R.D. Harris
Author:
C. Maciag
Author:
B.J. Luff
Author:
J. Piehler
Author:
A. Brecht
Author:
G. Gauglitz
Author:
R. Abuknesha
Author:
G. Ismail
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