A spectrofluorimetric method for the direct analysis of carbendazim [methyl 2-benzimidazole carbamate (MBC)] fungicide and its metabolite 2-aminobenzimidazole (2-AB) in natural waters is described. Very low limit of detection (LOD) and limit of quantification (LOQ) values of 0.002 - 0.06 ng/mL and 0.006 - 0.2 ng/mL, respectively, were determined by spectrofluorimetric method with small relative standard deviation (RSD) values < 1%. This spectrofluorimetric method was applied to the determination of MBC and 2-AB residues in natural waters, with satisfactory recovery values of (88.5% - 119.2%).
The carbendazim [methyl 2-benzimidazole carbamate (MBC)] is a fungicide that is introduced to control various vegetable and orchard diseases. MBC has been shown to be the solvolysis product of benomyl [
In this work, we are interested to the analysis of MBC and its metabolite 2-AB largely utilized in Senegal in vegetable crops. In order to control and eradicate pests, a great variety of pesticides are applied to both rural and urban zones throughout the world. In Senegal, most of the pulverized antiparasitic compounds are widely utilized in a peri-urban agricultural area, called the “Niayes area”, where cultures are practiced during all seasons, and where most fruits and vegetables consumed in Senegal are collected. Because of the number of pesticides utilized in the Niayes area and their persistence, serious problems related to chemical pollution and natural water contamination affect its aquatic ecosystem. In consequence, the development of sensitive, selective and precise analytical methods, able to determine the quantity of pesticide residues present in the environment, is necessary.
It is for this reason that we have undertaken a study on the MBC fungicide and its metabolite 2-AB by fluorescence method and we apply the analytical method to the evaluation of fungicide residues in spiked natural waters collected in the Niayes area.
MBC (98% m/m) and 2-AB (>97% m/m) were purchased from Sigma-Aldrich Chemical Company (USA) and were used without further purification. Spectroscopic grade solvent including dichloromethane (DCM), acetoni- trile and dimethyl sulfoxide (DMSO) were obtained from Sigma Aldrich (France). Ethanol was purchased from Prolabo (France), and borate buffer solutions of different pH values (4, 7 and 10) were from Cluzeau Info Labo. The chemical structure of benzimidazoles is presented in
All spectral measurements were performed at room temperature with a Varian Cary Eclipse Fluorescence Spectrophotometer interfaced with a microcomputer and processed by software FL-WinLab. Standard quartz fluorescence with a 1-cm path lengths (Labo Moderne, France) were used for measurements and a Pipetman of 10 - 1000 µL (Gilson, France) was used for dilutions. The non-purgeable organic carbon (NPOC) was measured on Total Organic Analyzer Shimadzu (TOC-VCSH/CSN). The pH measurements were performed with a Consort pH-meter Model P107. The conductivity was recorded on CDM 92, 2-pole Conductivity Cells Radiometer Analytical.
Stock standard solutions of the fungicides (191.2 mg/L for MBC and 133.15 mg/L for 2-AB) were freshly prepared by dissolving the compound in acetonitrile. Serial dilutions were performed to obtain working solutions. All solutions were protected against light with aluminum foil and were stored in a refrigerator at 6˚C for further use.
An aliquot of fungicide working solution was placed in a quartz cuvette, and the fluorescence spectra were recorded at a scanning speed of 600 nm/min. Fluorescence intensity was monitored at fixed analytical excitation (lex) and emission (lem) maximum wavelengths of the fungicide by measuring the spectra height signal. All fluorescence measurements were corrected for the solvent (background) signal with the appropriate blank.
Natural water samples were collected in 1.5-L amber glass bottles from natural waters (draining, well waters),
located inside and on the limits of the agricultural Niayes area. All samples were filtered through a Syringe Filter PTFE membrane, diameter 25 mm pore size 0.2 μm (Sigma-Aldrich) in order to remove any suspended organic matter.
A reversed phase C18 SPE cartridge was conditioned with 5 mL of acetonitrile taking into consideration keeping the cartridge wet. Then 5 mL of the spiked water samples (2, 6 and 10 ng/mL for MBC or 0.6, 1.2 and 1.8 ng/mL for 2-AB) was loaded and the retained compounds were eluted by 4 mL of acetonitrile. The solid phase extraction method, were able to extract the MBC and 2-AB in the various water samples.
MBC and 2-AB were naturally fluorescent in the different media under study. In order to choose the optimized medium for the fluorescence determination of both pesticides, we decided to investigate the influence of the organic solvent and pH effect in pure aqueous solvent and we developed afterward, a valid quantitative analytical procedure for the direct spectrofluorimetric determination of MBC and 2-AB after solid-phase extraction (SPE) procedure.
The solvent effect on fluorescence spectra is of particular importance. A change in solvent is accompanied by a change in polarity of the surrounding medium. We have studied the fluorescence emission spectra of MBC and 2-AB in several organic solvents of different polarities and checked the pH effect in aqueous solutions.
We investigated the fluorescence behaviour of MBC and its metabolite 2-AB in several solvents of strongly different polarities, including, dichloromethane, ethanol, acetonitrile, DMSO. The results concerning the MBC and 2-AB spectral and chemical properties (λex, λem and IF) in these different media are reported in
The excitation maximum wavelengths presented two main bands in the regions 218 - 260 and 275 - 290 nm, whereas the emission maximum wavelengths occurred in the range 300 - 323 nm, according to the solvent and the compound (
The emission band of MBC shows minor variations with increasing solvent polarity; the maximum bathochromic shift being 12 nm. The emission band for 2-AB is more sensitive to solvents and presents a maximum red-shift value of 23 nm for the different solvents. The fluorescence intensity is much higher in DMSO and acetonitrile than the others media (
On the other hand, the variation of the fluorescence intensity of MBC and 2-AB as a function of the pH (curve not shown) was characterized by well defined maximum values of pH obtained at acid medium for MBC and neutral for 2-AB. The effect of pH has allowed us to know that the analysis of MBC and 2-AB by fluorescence in water is most appropriate in a strongly acid (pH = 4) and neutral (pH = 7) medium, respectively, for MBC and 2-AB.
In order to select the most interesting conditions from the analytical standpoint, we optimized our spectrofluori- metric method for MBC and 2-AB determination by comparing the IF values in the various media under study. Relative to the fungicides fluorescence signal in DCM, which was used as a reference medium, the highest IF
Solvent | MBC | 2-AB | ||||
---|---|---|---|---|---|---|
lEmaxa | lFmaxb | IFc | lEmaxa | lFmaxb | IFc | |
DCM | 275 | 300 | 1.0 | 275 | 300 | 1.0 |
Ethanol | 285 | 306 | 3.4 | 284 | 315 | 3.0 |
Acetonitrile | 285 | 306 | 4.1 | 284 | 314 | 4.2 |
DMSO | 289 | 312 | 4.8 | 290 | 323 | 4.9 |
Water (pH =7) | 218 | 306 | 2.6 | 234 | 303 | 4.0 |
Water (pH = 4) | 275 | 304 | 3.9 | 275 | 304 | 3.4 |
Water (pH = 10) | 285 | 311 | 1.7 | 284 | 319 | 2.0 |
aWavelength of fluorescence excitation maxima (nm); bWavelength of fluorescence emission maxima (nm); cRelative fluorescence intensity, normalized to the fluorescence intensity in DCM.
values were found in DMSO, acetonitrile and water at pH = 4 and 7. Therefore, for comparison purposes, we decided to evaluate the analytical figures of merit of the fungicide MBC and its metabolite in these selected media, namely DMSO, acetonitrile and in water at pH = 4 and 7 (
The data summarized in
The reproducibility of measurements, evaluated with freshly-prepared MBC and 2-AB solutions, was satisfactory, as indicated by the small relative standard deviation (RSD) values less than 1%. The LODs were significantly low, ranging from 0.01 to 0.06 ng/mL for MBC and 0.002 to 0.01 ng/mL for 2-AB. The corresponding limit of quantification (LOQ) were 0.03 - 0.2 ng/mL for MBC and 0.006 - 0.03 ng/mL for 2-AB (
Compound | solvent | LOD (ng/mL)a | LOQ (ng/mL)b | LDR (ng/mL)c | RSD (%)d | r2e |
---|---|---|---|---|---|---|
MBC | Acetonitrile | 0.02 | 0.06 | 0.4 - 20 | 0.5 | 0.998 |
Water (pH = 4) | 0.06 | 0.2 | 0.6 - 20 | 0.8 | 0.997 | |
DMSO | 0.01 | 0.03 | 0.4 - 20 | 0.7 | 0.998 | |
2-AB | Acetonitrile | 0.005 | 0.02 | 0.1 - 10 | 0.6 | 0.997 |
Water (pH = 7) | 0.01 | 0.03 | 0.4 - 10 | 0.6 | 0.997 | |
DMSO | 0.002 | 0.006 | 0.1 - 10 | 0.7 | 0.998 |
aLimit of detection was defined as the amount of analyte giving a signal-to-noise ratio of 3; bLimit of quantification defined as the amount of analyte giving a signal-to-noise ratio of 10; cLinear dynamic range; dRelative standard deviation (n = 6); eCorrelation coefficient.
Our direct fluorimetric method developed, has limits of detection lower than those reported by authors using various methods, such as dispersive liquid-liquid microextraction (DLLME) combined with UV-Vis spectrophotometry (LOD = 2.1 ng/mL) [
Solvent effect has shown that MBC and 2-AB have high fluorescence signal in DMSO, acetonitrile and water (pH = 4 and 7). Because of its viscosity, DMSO can neither be used to pack the column nor to elute MBC and 2-AB. The elution of the two benzimidazoles with water (pH = 4 and 7) gives also poor percentages of recovery with spectra deformation. As a result, we used acetonitrile as packing and elution solvent to extract the fungicide MBC and 2-AB by SPE.
We studied the effect of the volume of the elution solvent on the extraction efficiency for different volumes of the solvent acetonitrile (0.5, 1, 2, 3, 4, 5, 5.5, 6 mL) and the recovery percentage was determined at the same time.
To verify the applicability of the proposed direct spectrofluorimetric method to authentic samples, MBC and 2-AB were determined in natural water samples after a Solid-Phase extraction (SPE) procedure. For recovery studies, 5 mL of water samples were spiked at three different concentration levels of each pesticide. We used acetonitrile as a packing solvent and as a solvent of elution to extract the fungicide MBC and 2-AB. Acetonitrile gave good percentage recovery. The results obtained in the different water samples are satisfactory because the recovery rate varies between 88.5% and 119.2% (
On the other hand, the physicochemical parameters of the natural water samples including the dissolved organic carbon NPOC (mg/L), the conductivity s (ms/cm) and the pH (
Since, the amount of dissolved organic matters in the natural water samples plays a certain role on the rate of recovery of both benzimidazoles, we decided to study the effect of foreign species and of some inorganic ions on the fluorescence intensity of the MBC in water (pH = 4) and of 2-AB in water (pH = 7).
The effect of some pesticides such as benomyl, thiabendazole (commonly-used in Senegal) and several inorganic ions including Na+, Ca2+, K+, Cl−,
Matrice | MBC | 2-AB | ||||||
---|---|---|---|---|---|---|---|---|
Added (ng/mL) | Found (n = 3) (ng/mL) | Recovery (%) | Mean recovery ± SD | Added (ng/mL) | Found (n = 3) (ng/mL) | Recovery (%) | Mean recovery ± SD | |
Draining water | 2 | 2.27 | 113.5 | 111.3 ± 2.2 | 0.6 | 0.68 | 113.3 | 116.6 ± 2.4 |
6 | 6.72 | 112.0 | 1.2 | 1.43 | 119.2 | |||
10 | 10.84 | 108.4 | 1.8 | 2.11 | 117.2 | |||
Well water (d = 10 m) | 2 | 1.86 | 93.0 | 94.6 ± 1.2 | 0.6 | 0.56 | 93.3 | 97.2 ± 3.5 |
6 | 5.76 | 96.0 | 1.2 | 1.22 | 101.7 | |||
10 | 9.47 | 94.7 | 1.8 | 1.74 | 96.5 | |||
Well water (d = 1.5 m) | 2 | 1.87 | 93.5 | 96.8 ± 6.6 | 0.6 | 0.65 | 108.3 | 102.8 ± 4.1 |
6 | 5.16 | 106.0 | 1.2 | 1.22 | 101.7 | |||
10 | 9.10 | 91.0 | 1.8 | 1.77 | 98.3 | |||
Well water (d < 1 m) | 2 | 1.77 | 88.5 | 90.7 ± 1.5 | 0.6 | 0.57 | 95.0 | 96.5 ± 1.2 |
6 | 5.52 | 92.0 | 1.2 | 1.16 | 96.7 | |||
10 | 9.15 | 91.5 | 1.8 | 1.76 | 97.8 |
d = depth of the well water.
Water samples | NPOCa (mg/L) | sb (mS/cm) | pH |
---|---|---|---|
Draining water | 103.50 | 26.25 | 8.17 |
Well water (d = 10 m) | 8.99 | 2.91 | 8.24 |
Well water (d = 1.5 m) | 29.54 | 2.93 | 6.86 |
Well water (d < 1 m) | 9.94 | 2.94 | 7.33 |
aNPOC (mg/L) = dissolved organic carbon, corresponding to the non-purgeable organic carbon present in natural waters. Calculated from the equation: NPOC = TOC − POC, with NPOC = non-purgeable organic carbon, TOC = total organic carbon and POC = purgeable organic carbon; bσ (mS/cm) = conductivity of the water samples.
The tolerance limit obtained for the selected foreign species are presented in
An increase or decrease in intensity was observed during the addition of pesticides or inorganic ions in the studied concentration range. The observed phenomenon may be due to direct interactions between foreign species (pesticides or inorganic ions) with MBC or 2-AB. Our results showed that all tested foreign species have interference on the MBC and the 2-AB. The most important effect of interference on the MBC was observed with benomyl (tolerance limit = 0.05 ng/mL) and 2-AB (tolerance limit = 0.07 ng/mL). For the 2-AB, the effect of the higher interference was observed with benomyl (tolerance limit = 0.06 ng/mL) and MBC (tolerance limit = 0.06 ng/mL). These limits correspond to concentrations about 40 times lower than that of MBC and 10 times
Foreign species | Interference with MBC | Interference with 2-AB | ||
---|---|---|---|---|
Tested concentration range (ng/mL) | Tolerance limit (ng/mL) | Tested concentration range (ng/mL) | Tolerance limit (ng/mL) | |
MBC | ----- | ---- | 0.01-1 | 0.06 |
2-AB | 0.02 - 4 | 0.07 | ----- | ----- |
Benomyl | 0.02 - 4 | 0.05 | 0.01 - 1 | 0.06 |
Thiabendazole | 0.02 - 4 | 0.1 | 0.01 - 1 | 0.09 |
0.05 - 4 | 1.8 | 0.05 - 1 | 0.4 | |
0.05 - 4 | 1.2 | 0.05 - 1 | 0.1 | |
0.05 - 4 | 1.6 | 0.05 - 1 | 0.5 | |
0.05 - 4 | 1.9 | 0.05 - 1 | 0.7 | |
0.05 - 4 | 1.3 | 0.05 - 1 | 0.4 |
lower than that of 2-AB. These results can be explained by the fact that benomyl is a compound that is metabolized to MBC during ordinary analytical procedures in organic solvents and water [
We have shown the usefulness of the effect of organic solvent and pH for improving the sensitivity of the florescence detection of MBC and 2-AB. In this work, we developed a simple, sensitive and precise fluorescence method for the determination of fungicide MBC and its metabolite 2-AB in Senegal natural water samples. Excellent analytical results have been obtained, which permit to detect and quantify MBC and 2-AB at very low concentrations, in the ng/L range, with satisfactory recovery values in natural water samples.
Diène Diégane Thiaré would like to thanks the Service of Cooperation and Cultural Action of the Embassy of France for financial support during his stay in the University of the Littoral Côte d’Opale at Dunkerque (France).
Diène DiéganeThiaré,AbdourakhmaneKhonté,AmadouDiop,AlphonseMendy,AtanasseColy,FrançoisDelattre,Mame DiabouGaye-Seye,AlphonseTine, (2015) Spectrofluorimetric Analysis of the Fungicide Carbendazim and Its Metabolite 2-Aminobenzimidazole in Natural Water. American Journal of Analytical Chemistry,06,767-775. doi: 10.4236/ajac.2015.69073