Seasonal distribution of multiclass pesticide residues in the surface waters of northwest Croatia
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30 dic 2021
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Categoría del artículo: Original article
Publicado en línea: 30 dic 2021
Páginas: 280 - 288
Recibido: 01 oct 2021
Aceptado: 01 nov 2021
DOI: https://doi.org/10.2478/aiht-2021-72-3598
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© 2021 Heinz-Elmar Tenorth, published by Sciendo
This work is licensed under the Creative Commons Attribution-NonCommercial-NoDerivatives 3.0 License.
Figure 1

Figure 2

Mass concentrations of pesticide pollutants in river/stream water samples collected in the northwest part of Croatia across application season
Pesticide compound | March 2015 (N=8) | June 2015 (N=8) | August 2015 (N=7) | ||||||
---|---|---|---|---|---|---|---|---|---|
Rangea | Medianb | Rangea | Medianb | Rangea | Medianb | ||||
Mesotrione | 0 | 3 | 36–107 | 0 | 0 | ||||
Tembotrione | 0 | 7 | 51–216 | 77 | 0 | ||||
AMBA | 0 | 6 | 54–444 | 74 | 1 | 61 | <LOD | ||
Terbuthylazine | 3 | 9–13 | <LOD | 8 | 20–419 | 42 | 5 | 10–26 | 13 |
DET | 1 | 9 | <LOD | 4 | 38–200 | 19 | 2 | 14–45 | <LOD |
Atrazine | 5 | 10–16 | 11 | 5 | 12–34 | 13 | 5 | 9–24 | 14 |
DIA | 5 | 5–32 | 6 | 6 | 17–123 | 28 | 2 | 19–24 | <LOD |
DEA | 4 | 8–11 | 4 | 7 | 7–24 | 11 | 5 | 6–32 | 10 |
Isoproturon | 1 | 146 | <LOD | 0 | 0 | ||||
Diuron | 0 | 2 | 22–30 | <LOD | 0 | ||||
Acetochlor | 0 | 1 | 28 | <LOD | 0 | ||||
Metolachlor | 7 | 9–11 | 9 | 8 | 11–3015 | 147 | 6 | 10–63 | 11 |
Chlorpyrifos-methyl | 0 | 1 | 26 | <LOD | 0 | ||||
Chlorpyrifos-methyl-oxon | 1 | 21 | <LOD | 8 | 23–145 | 64 | 3 | 34–198 | <LOD |
Imidacloprid | 1 | 73 | <LOD | 8 | 12 – 34 | 26 | 0 |
Methods for determination of pesticides and their degradation products in natural waters by SPE and HPLC-UV(DAD) or GC-MS(ITD) analysis
Method of analysis | HPLC-UV(DAD) | GC-MS(ITD) | |||
---|---|---|---|---|---|
Pesticide | Mesotrione – 220 | Terbuthylazine – 222 | Atrazine – 222 | Trifluralin – 264 | Terbuthylazine – 214 |
AMBA – 220 | DET – 214 | DEA – 214 | Atrazine – 200 | Chlorpyrifosmethyl – 286 | |
Tembotrione – 205 | Malathion – 205 | DIA – 214 | Terbuthylazine – 214 | Chlorpyrifosethyl – 314 | |
Chlorfenvinphos – 205 | Terbuthylazine – 222 | Acetochlor – 223 | Malathion – 173 | ||
Chlorpyrifos-methyloxon – 205 | DET – 214 | Alachlor – 188 | Chlorfenvinphos – 267 | ||
Imidacloprid – 270 | Diuron – 210, 245 | Metolachlor – 162 | α-Cypermethrin – 163 | ||
Linuron – 210, 245 | |||||
Chlortoluron – 210, 245 | |||||
Isoproturon – 202, 245 | |||||
SPE | OASIS HLB | C18 | SDB-1 | C18 | C18 Polar plus/ SDB-1 |
Activation | MeOH+H2O | ACN+H2O | MeOH+H2O | MeOH+H2O | MeOH+H2O |
Solvent volume (mL) | 2+2 | 5+5 | 2+5 | 2+5 | 2+5 |
Sample volume (mL) | 500 | 500 | 500 | 1000 | 500 |
Eluent | MeOH | ACN+Et.ac | Ac | Et.ac | Et.ac |
Eluent volume (mL) | 10 | 10+5 | 2 | 2 | 10 |
Number (N) of individual pesticide compounds, their mass concentration range, and the sum of pesticides mass concentrations (Σ) by river/stream across application season
River/Stream | March 2015 | June 2015 | August 2015 | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
Min | Max | Σ | Min | Max | Σ | Min | Max | Σ | ||||
Sutla | 3 | 8 | 22 | 41 | 9 | 9 | 2564 | 3 | 10 | 63 | 99 | |
Krapina | 7 | 9 | 146 | 219 | 10 | 22 | 3015 | 5 | 6 | 198 | 248 | |
Sava 1 | 2 | 9 | 73 | 81 | 11 | 10 | 242 | 4 | 9 | 45 | 77 | |
Sava 2 | 4 | 6 | 11 | 35 | 11 | 7 | 149 | 498 | – not analysed – | |||
Drava | 2 | 5 | 10 | 15 | 6 | 22 | 86 | 323 | 2 | 11 | 14 | 25 |
Plitvica | 2 | 10 | 16 | 25 | 7 | 16 | 115 | 331 | 4 | 10 | 32 | 76 |
Bistrica | 3 | 9 | 32 | 52 | 10 | 11 | 216 | 5 | 13 | 61 | 147 | |
Bednja | 5 | 7 | 16 | 56 | 10 | 12 | 444 | 6 | 11 | 66 | 161 |
Pesticides and pesticide degradation products analysed in this study
Class/Pesticide | Chemical name | log |
pKa |
|
---|---|---|---|---|
Trifluralin | 2,6-dinitro- |
0.221 | 5.27 | ND |
Atrazine | 6-chloro- |
35 | 2.7 | 1.7 |
Deethylatrazine (DEA) | 6-chloro- |
2700 | 1.51 | 1.3 |
Deisopropylatrazine (DIA) | 6-chloro- |
980 | 1.15 | 1.2 |
Terbuthylazine | 6-chloro- |
6.6 | 3.4 | 1.9 |
Deethylterbuthylazine (DET) | 6-chloro- |
327.1 | 2.3 | 1.35 |
Diuron | 3-(3,4-dichlorophenyl)-1,1-dimethylurea | 35.6 | 2.87 | ND |
Linuron | 3-(3,4-dichlorophenyl)-1-methoxy-1-methylurea | 63.8 | 3.0 | ND |
Chlortoluron | 3-(3-chloro-4-methylphenyl)-1,1-dimethylurea | 76 | 2.5 | ND |
Isoproturon | 3-(4-isopropylphenyl)-1,1-dimethylurea | 70.2 | 2.5 | ND |
Acetochlor | 2-chloro- |
282 | 4.14 | ND |
Alachlor | 2-chloro- |
240 | 3.09 | 0.62 |
Metolachlor | ( |
530 | 3.4 | ND |
Mesotrione | 2-[4-(methylsulfonyl)-2-nitrobenzoyl]cyclohexane-1,3-dione | 1500 | 0.11 | 3.12 |
2-Amino-4-(methylsulfonyl) benzoic acid (AMBA) | 2-amino-4-(methylsulfonyl)benzoic acid | NA | 0.38 |
4.24 |
Tembotrione | 2-[2-chloro-4-methylsulfonyl-3-(2,2,2-trifluoroethoxymethyl) benzoyl]cyclohexane-1,3-dione | 71000 | -1.09 | 3.18 |
Chlorpyrifos-methyl | 2.74 | 4.00 | ND | |
Chlorpyrifos-ethyl | 1.05 | 4.7 | ND | |
Chlorpyrifos-methyl-oxon | Dimethyl (3,5,6-trichloropyridin-2-yl) phosphate | NA | 1.91 |
NA |
Malathion | Diethyl 2-[(dimethoxyphosphorothioyl)sulfanyl]butanedioate | 148 | 2.75 | ND |
Chlorfenvinphos | [( |
145 | 3.8 | ND |
α-Cypermethrin | Racemate comprising |
0.004 | 5.8 | ND |
Imidacloprid | 610 | 0.57 | ND |