Research Article
Photocatalytic Degradation of Pesticides in Natural Water: Effect of Hydrogen Peroxide
Table 3
Results of the methodology validation of the pesticide analysis.
| Pesticide | Quantification limit (μg L−1) |
Calibration interval (μg L−1) |
Validity interval (μg L−1) | Recovery interval (%) | Instrumental step | Full method | Instrumental step | Full method |
| Isoproturon | 20 | 0.030 | 20–500 | 0.030–300 | 75–130 | 63–110 | Diuron | 20 | 0.030 | 20–500 | 0.030–300 | 82–128 | 70–123 | 3,4-Dichloroaniline | 20 | 0.030 | 20–500 | 0.030–300 | 88–130 | 47–106 | 4-Isopropylaniline | 20 | 0.030 | 20–500 | 0.030–300 | 80–130 | 60–125 | Desethylatrazine | 20 | 0.030 | 20–500 | 0.030–300 | 76–130 | 80–129 | Trifluralin | 20 | 0.015 | 20–500 | 0.030–300 | 70–130 | 70–127 | Dimethoate | 20 | 0.030 | 50–500 | 0.030–300 | 66–124 | 54–137 | Simazine | 50 | 0.030 | 20–500 | 0.030–600 | 75–135 | 64–127 | Prometon | 20 | 0.030 | 20–500 | 0.030–300 | 76–124 | 0–125 | Atrazine | 200 | 0.100 | 200–5000 | 0.100–300 | 78–130 | 75–127 | Propazine | 20 | 0.015 | 20–500 | 0.015–300 | 86–130 | 73–127 | Terbuthylazine | 20 | 0.015 | 20–500 | 0.015–300 | 79–130 | 83–128 | Parathion methyl | 50 | 0.030 | 50–500 | 0.030–300 | 78–139 | 72–130 | Parathion ethyl | 20 | 0.030 | 20–500 | 0.030–300 | 74–122 | 64–128 | Alachlor | 20 | 0.015 | 20–500 | 0.015–300 | 75–125 | 70–124 | Ametryn | 20 | 0.030 | 20–500 | 0.030–300 | 78–130 | 0–116 | Prometryn | 20 | 0.030 | 20–500 | 0.030–300 | 80–120 | 17–116 | Terbutryn | 20 | 0.030 | 20–500 | 0.030–300 | 80–120 | 13–114 | Chlorpyrifos | 20 | 0.015 | 20–500 | 0.015–300 | 75–120 | 73–116 | Chlorfenvinfos | 20 | 0.015 | 20–500 | 0.015–300 | 76–130 | 70–126 | HCHs | 20 | 0.015 | 20–500 | 0.015–300 | 84–124 | 70–120 | Hexachlorobenzene | 20 | 0.030 | 20–500 | 0.030–300 | 70–130 | 74–136 | Heptachlor | 20 | 0.015 | 20–500 | 0.015–300 | 75–130 | 58–113 | Heptachlor epoxide A | 20 | 0.015 | 20–500 | 0.015–300 | 85–125 | 62–112 | Heptachlor epoxide B | 20 | 0.015 | 20–500 | 0.015–300 | 84–130 | 58–113 | Aldrin | 20 | 0.015 | 20–500 | 0.015–300 | 85–125 | 64–126 | 4,4′-Dichlorobenzophenone | 20 | 0.015 | 20–500 | 0.015–300 | 75–120 | 68–126 | Isodrin | 20 | 0.015 | 20–500 | 0.015–300 | 85–125 | 66–120 | α-Endosulphan | 20 | 0.015 | 20–500 | 0.015–300 | 70–125 | 70–93 | pp′-DDE | 20 | 0.015 | 20–500 | 0.015–300 | 89–122 | 64–107 | Dieldrin | 20 | 0.015 | 20–500 | 0.015–300 | 70–125 | 62–120 | Endrin | 20 | 0.015 | 20–500 | 0.015–300 | 80–125 | 74–122 | pp′-DDD + op′-DDT | 40 | 0.030 | 40–1000 | 0.030–600 | 79–125 | 66–139 | Endosulphan-sulphate | 20 | 0.015 | 20–500 | 0.015–300 | 83–125 | 73–126 | pp′-DDT | 20 | 0.030 | 20–500 | 0.030–300 | 76–130 | 50–120 | Dicofol | 50 | 0.030 | 50–500 | 0.030–300 | 80–148 | 63–136 | Methoxychlor | 20 | 0.015 | 20–500 | 0.015–300 | 77–126 | 75–130 | Metholachlor | 20 | 0.015 | 20–500 | 0.015–300 | 76–115 | 73–128 | Molinate | 20 | 0.015 | 20–500 | 0.015–300 | 91–130 | 75–113 | Tetradifon | 20 | 0.015 | 20–500 | 0.015–300 | 85–130 | 70–116 |
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