Transfer Pathways and Fluxes of Water-Soluble Pesticides in Various Compartments of the Agricultural Catchment of the Canche River (Northern France)
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Supplementary Materials: Transfer Pathways and Fluxes of Water-Soluble Pesticides in Various Compartments of the Agricultural Catchment of the Canche River (Northern France) Angel Belles 1, Claire Alary 2, Agnès Rivière 1, Sophie Guillon 1, Edouard Patault 1,2,3, Nicolas Flipo 1 and Christine Franke 1,* 1 Center of Geosciences, PSL Research University, MINES ParisTech, 35 rue St. Honoré, F-77305 Fontainebleau Cedex, France; [email protected] (A.B.); [email protected] (A.R.); [email protected] (S.G.); [email protected] (N.F.) 2 IMT Lille Douai, Univ. Lille, EA 4515 - LGCgE, F-59000 Lille, France; [email protected] 3 Normandie Univ, UNIROUEN, UNICAEN, CNRS, M2C, FED-SCALE, F-76821 Rouen, France; [email protected] (E.P.) * Correspondence: [email protected] Content: Table S1: GPS coordinates of sampling sites. Table S2: Dissolved concentrations of pesticides during the seasonal campaign (ng L−1). Table S3: Herbicides flux during the seasonal campaigns (g day−1). Table S4: Mass balance analysis: discrepancy between the tributaries and the closest effluent point (%). Table S5: Specific fluxes during the seasonal campaigns (mg day−1 km−2). Table S6: Dissolved concentrations of pesticides at Canche 5 sampling site (ng L−1). Table S7: Average dissolved concentrations of pesticides at Canche 5 sampling site (passive samplers; ng L−1). Table S8: Dissolved concentrations of pesticides in ground water during summer and winter (ng L−1). Figure S1: Comparison between the measured water discharge at Course gauging station and the estimation method using as reference the gauging station on the main stream. Figure S2: Transport kinetics of diflufenican from the SPM-sorbed state to the dissolved phase. Figure S3. Dissolved concentration measured at Canche 5 sampling site. Figure S4. Dissolved concentration of atrazine at pz7 sampling point (groundwater). Water 2018, 10, x FOR PEER REVIEW S2 of S11 Table S1. GPS coordinates of sampling sites. river/site longitude latitude Canche 0 50°22’43.1”N 2°01’03.5”E Ternoise 50°22’47.6”N 2°02’33.7”E Canche 1 50°23’09.0”N 1°59’59.6”E Planquette 50°24’26.0”N 1°58’11.0”E Canche 2 50°24’45.5”N 1°55’43.3”E Créquoise 50°25’49.5”N 1°54’23.2”E Canche 3 50°25’57.2”N 1°53’37.6”E Bras de Bronne 50°27’22.0”N 1°49’32.6”E Canche 4 50°27’32.0”N 1°47’58.7”E Course 50°28’50.7”N 1°45’51.9”E Canche 5 50°28’41.1”N 1°44’55.9”E Dordogne 50°30’01.4”N 1°42’28.4”E Canche 6 50°29’39.5”N 1°41’11.8”E Huîtrepin 50°30’15.6”N 1°41’30.5”E Canche 7 50°30’10.8”N 1°40’24.4”E Table S2. Dissolved concentrations of pesticides during the seasonal campaign (ng L−1). Créquoise Créquoise Dordogne Huîtrepin Huîtrepin Planquett Canche 0 Canche 1 Canche 2 Canche 3 Canche 4 Canche 5 Canche 6 Canche 7 Ternoise Bras de Brônne Course e atrazine 11 10 10 13 18 17 16 8 9 9 8 10 12 12 11 diflufenican 3 3 1 2 2 9 3 2 3 2 2 2 2 3 3 ethofumesathe <1 <1 <1 <1 <1 2 2 <1 <1 <1 <1 <1 <1 1 1 metolachlor 1 3 1 1 2 1 2 1 1 1 1 1 1 2 2 February 16 pendimethalin <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 atrazine 14 13 13 19 21 19 19 11 13 13 13 11 10 11 11 diflufenican 2 2 2 2 4 8 4 2 2 2 3 3 3 3 3 ethofumesathe 27 8 37 10 25 3 6 7 11 12 14 11 8 10 12 May 16 May metolachlor 5 6 352 3 3 2 41 3 5 6 39 33 22 20 15 pendimethalin <1 <1 <1 <1 <1 1 1 5 2 2 2 2 2 1 1 atrazine 13 11 11 17 16 15 16 10 13 11 11 12 12 12 13 diflufenican <1 1 <1 1 1 2 2 1 1 1 1 1 1 1 1 ethofumesathe 1 <1 <1 <1 <1 1 1 1 <1 <1 1 1 1 1 1 July 16 metolachlor 7 2 2 5 2 1 2 3 3 3 2 4 3 2 2 pendimethalin <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 atrazine 13 9 9 10 14 9 11 9 11 10 8 7 10 12 12 diflufenican 3 34 5 21 4 52 25 9 5 7 4 5 4 7 9 ethofumesathe <1 <1 <1 3 <1 6 2 <1 <1 <1 <1 <1 <1 <1 <1 metolachlor <1 2 <1 2 1 4 4 2 <1 <1 <1 <1 1 1 5 November 16 pendimethalin 4 5 24 28 18 101 27 3 3 4 5 7 9 13 11 Water 2018, 10, x FOR PEER REVIEW S3 of S11 Table S3. Herbicides fluxes calculated during the seasonal campaigns (g day−1). Planquette Planquette Créquoise Créquoise Dordogne Huîtrepin deBrônne Canche 0 Canche 1 Canche 2 Canche 3 Canche 4 Canche 5 Canche 6 Canche 7 Ternoise Course Bras Water 7 1 2 2 6 2 2 9 16 17 19 20 26 28 29 discharge (m3 s−1) atrazine 6.6 1.0 1.4 1.8 8.5 3.0 2.2 6.1 12.2 12.9 12.4 17.9 27.2 28.0 28.2 diflufenican 1.7 0.3 0.1 0.3 1.0 1.5 0.4 1.9 3.7 3.6 3.8 4.1 4.4 7.1 7.5 ethofumesathe <0.2 <0.1 <0.1 <0.2 <0.2 0.4 0.2 <0.3 <0.5 <0.5 <0.5 <0.6 <0.8 1.3 1.3 February 16 February metolachlor 0.7 0.3 0.1 0.2 0.9 0.2 0.2 0.7 1.3 1.6 2.0 2.1 2.9 4.1 4.0 pendimethalin <0.2 <0.1 <0.1 <0.2 <0.2 <0.2 <0.2 <0.3 <0.5 <0.5 <0.5 <0.6 <0.8 <0.8 <0.9 Water 5 1 1 1 4 1 1 7 13 13 15 16 20 21 22 discharge (m3 s−1) atrazine 6.5 1.0 1.4 1.8 6.6 2.2 1.7 6.6 14.4 15.1 16.0 15.5 16.5 19.8 21.0 diflufenican 1.1 0.1 0.2 0.2 1.2 0.9 0.3 1.4 2.7 2.6 3.3 3.6 4.3 5.4 5.7 May 16 ethofumesathe 12.3 0.6 4.0 1.0 7.7 0.3 0.6 4.6 12.2 13.4 17.5 15.1 13.8 18.1 22.7 metolachlor 2.2 0.4 37.7 0.3 0.9 0.2 3.7 1.8 5.3 7.0 50.1 45.6 37.3 36.2 28.5 pendimethalin <0.2 <0.1 <0.1 <0.2 <0.2 0.1 0.8 2.9 1.9 2.3 2.5 2.8 3.4 1.8 2.1 Water 5 1 1 1 3 1 1 5 10 11 12 13 16 17 18 discharge (m3 s−1) atrazine 5.2 0.8 1.0 1.3 4.2 1.3 1.1 4.7 11.1 10.0 11.4 13.0 15.9 17.8 20.0 diflufenican <0.2 <0.1 <0.1 0.1 0.2 0.2 0.1 0.5 0.5 0.5 0.6 0.7 1.0 0.9 1.0 July 16 July ethofumesathe 0.2 <0.1 <0.1 <0.2 <0.2 0.1 0.8 0.3 <0.5 <0.5 0.5 0.6 1.0 0.8 0.9 metolachlor 2.7 0.1 0.2 0.4 0.4 0.1 0.1 1.3 2.6 2.7 2.4 4.5 4.7 2.9 2.3 pendimethalin <0.2 <0.1 <0.1 <0.2 <0.2 <0.2 <0.2 <0.3 <0.5 <0.5 <0.5 <0.6 <0.8 <0.8 <0.9 Water 4 1 1 1 2 1 1 5 8 9 10 11 13 14 14 discharge (m3 s−1) atrazine 4.1 0.5 0.7 0.6 2.8 0.6 0.6 3.8 7.8 8.0 6.8 6.5 10.9 14.1 15.3 diflufenican 1.1 1.8 0.4 1.3 0.8 3.7 1.4 3.5 3.4 5.1 3.5 4.4 4.7 7.7 11.3 ethofumesathe <0.2 <0.1 <0.1 0.2 <0.2 0.4 0.1 <0.3 <0.5 <0.5 <0.5 <0.6 <0.8 <0.8 <0.9 November 16 November metolachlor <0.2 0.1 <0.1 0.1 0.3 0.3 0.2 0.7 <0.5 <0.5 <0.5 <0.6 0.9 1.0 6.3 pendimethalin 1.3 0.3 1.8 1.7 3.6 7.2 1.5 1.3 2.5 2.9 4.7 5.9 10.0 14.8 14.2 Water 2018, 10, x FOR PEER REVIEW S4 of S11 Table S4.