Graph -1. 2 hr acute toxicity exposure of Thiodan (Endosulfan % EC) to freshwater Regression equation Y= -1.10 + 0.1 9% Fiducial limits, 0.0 to 0.098 ppm. Calculated LC0= 0. ppm. 0 0.02 0.0 0.0 0.08 0.1 0.12 0.1 Graph -2 8 hr acute toxicity exposure of Thiodan (Endosulfan % EC) to freshwater Regression equation Y= -1.028 + 0.209 X 9% Fiducial limits, 0.09 to 0.0 ppm. Calculated LC0= 0.09 ppm. 0 0.02 0.0 0.0 0.08 0.1
2 hr acute toxicity exposure of Thiodan (Endosulfan % EC) to freshwater Regression equation Y= -1.1 + 0.008 X 9% Fiducial limits, 0.02 to 0.00 ppm. Calculated LC0= 0.08 ppm. Graph- 0 0.02 0.0 0.0 0.08 0.1 0.12 Graph- 9 hr acute toxicity exposure of Thiodan (Endosulfan % EC) to freshwater Regression equation Y= -1.0 + 0.0 X 9% Fiducial limits, 0.021 to 0.00 ppm. Calculated LC0= 0.029 ppm. 0 0.02 0.0 0.0 0.08 0.1
Graph No. 2 hr acute toxicity exposure of Thiodan (Endosulfan % EC) to freshwater Regression equation Y= -1.1 + 0.19 X 9% Fiducial limits, 0.0 to 0.09 ppm. Calculated LC0= 0.09 ppm. 0 0.02 0.0 0.0 0.08 0.1 0.12 0.1 Graph No. 8 hr acute toxicity exposure of Thiodan (Endosulfan % EC) to freshwater Regression equation Y= -1.2 + 0.212 X 9% Fiducial limits, 0.08 to 0.09 ppm. Calculated LC0= 0.0 ppm. 0 0.02 0.0 0.0 0.08 0.1 0.12
Graph No. 2 hr acute toxicity exposure of Thiodan (Endosulfan % EC) to freshwater Regression equation Y= -1. + 0.289 X 9% Fiducial limits, 0.01 to 0.02 ppm. Calculated LC0= 0.0 ppm. 0 0.02 0.0 0.0 0.08 0.1 Graph No.8 9 hr acute toxicity exposure of Thiodan (Endosulfan % EC) to freshwater Regression equation Y= -1.80 + 0.202 X 9% Fiducial limits, 0.02 to 0.09 ppm. Calculated LC0= 0.02 ppm. 0 0.02 0.0 0.0 0.08 0.1
Graph No.9 2 hr acute toxicity exposure of Thiodan (Endosulfan % EC) to freshwater Lamellibranch bivalve mollusc, Lamellidense corrianus during summer. Regression equation Y= --2.1 + 0.200 X 9% Fiducial limits, 0.018 to 0.029 ppm. Calculated LC0= 0.021 ppm. 0 0.00 0.01 0.01 0.02 0.02 0.0 0.0 0.0 0.0 0.0 8 hr acute toxicity exposure of Thiodan (Endosulfan % EC) to freshwater Lamellibranch bivalve mollusc, Lamellidens corrianus during summer. Regression equation Y= -1.80 + 0.202 X 9% Fiducial limits, 0.02 to 0.09 ppm. Calculated LC0= 0.02 ppm. Graph No.10 0 0.00 0.01 0.01 0.02 0.02 0.0 0.0 0.0 0.0 0.0
Regression equation Y= --2. + 0.1 X 9% Fiducial limits, 0.001 to 0.002 ppm. Calculated LC0= 0.0021 ppm. Graph No.11 8 hr acute toxicity exposure of Thiodan (Endosulfan % EC) to freshwater Lamellibranch bivalve mollusc, Lamellidens corrianus during summer. 0 0.00 0.01 0.01 0.02 0.02 0.0 0.0 0.0 0.0 Graph No.12 9 hr acute toxicity exposure of Thiodan (Endosulfan % EC) to freshwater Lamellibranch bivalve mollusc, Lamellidens corrianus during summer. Regression equation Y= --2.02 + 0.08 X 9% Fiducial limits, 0.002 to 0.012 ppm. Calculated LC0= 0.008 ppm. 0 0.00 0.01 0.01 0.02 0.02 0.0 0.0 0.0
2 hr acute toxicity exposure of Ekalux (Quinolphos 2% EC), to freshwater Graph No.1. Regression equation Y=-1.218 + 0.10 X 9% Fiducial limits= 0.0 to 0.00 ppm. Calculated LC0= 0.00 ppm. 2. 1. 0 0.02 0.0 0.0 0.08 0.1 8 hr acute toxicity exposure of Ekalux (Quinolphos 2% EC), to freshwater Graph No.1. Regression equation Y =-1.281 + 0.10 X 9% Fiducial limits= 0.00 to 0.01 ppm. Calculated LC0=0.02 ppm. 2. 1. 0 0.02 0.0 0.0 0.08 0.1
2 hr acute toxicity exposure of Ekalux (Quinolphos 2% EC), to freshwater Graph No.1. Regression equation Y= -1. + 0.111X 9% Fiducial limits=0.0 to 0.0 ppm. Calculated LC0=0.0 ppm. 2. 1. 0 0.01 0.02 0.0 0.0 0.0 0.0 0.0 0.08 Graph No.1 9 hr acute toxicity exposure of Ekalux (Quinolphos 2% EC), to freshwater Regression equation Y= -1.28 + 0.199 X 9% Fiducial limits=0.0 to 0.0 ppm. Calculated LC0= 0.0 ppm. 2. 0 0.01 0.02 0.0 0.0 0.0 0.0 0.0
Graph No.1 2 hr acute toxicity exposure of Ekalux (Quinolphos 2% EC), to freshwater. Regression equation Y= -1.111 + 0.222 X 9% Fiducial limits, 0.08 to 0.099 ppm. Calculated LC0= 0.02 ppm. 2. 1. 0 0.0 0.1 0.1 0.2 0.2 8 hr acute toxicity exposure of Ekalux (Quinolphos 2% EC), to freshwater Graph No.18. Regression equation Y= -1.211 + 0.20 9% Fiducial limits, 0.028 to 0.09 ppm. Calculated LC0= 0.0 ppm. 2. 1. 0 0.02 0.0 0.0 0.08 0.1 0.12
Graph 19 2 hr acute toxicity exposure of Ekalux (Quinolphos 2% EC), to freshwater. Regression equation Y= -1.0 + 0.289 9% Fiducial limits, 0.08 to 0.0 ppm. Calculated LC0= 0.0 ppm. 2. 1. 0 0.02 0.0 0.0 0.08 0.1 0.12 Graph No.20 9 hr acute toxicity exposure of Ekalux (Quinolphos 2% EC), to freshwater. Regression equation Y= -1.91 + 0.1 9% Fiducial limits, 0.01 to 0.08 ppm. Calculated LC0= 0.00 ppm. 2. 1. 0 0.02 0.0 0.0 0.08 0.1
Graph No.21 2 hr acute toxicity exposure of Ekalux (Quinolphos 2% EC), to freshwater Lamellibranch bivalve mollusc, Lamellidense corrianus during summer. Regression equation Y= -2.1 + 0.200 X 9% Fiducial limits, 0.0018 to 0.0029 ppm. Calculated LC0= 0.0021 ppm. 0 0.01 0.02 0.0 0.0 0.0 Graph No.22 8 hr acute toxicity exposure of Ekalux (Quinolphos 2% EC), to freshwater Lamellibranch bivalve mollusc, Lamellidense corrianus during summer. Regression equation Y= -2. + 0.1 X 9% Fiducial limits, 0.001 to 0.002 ppm. Calculated LC0= 0.001 ppm. 0 0.00 0.01 0.01 0.02 0.02 0.0 0.0 0.0
Graph No.2 2 hr acute toxicity exposure of Ekalux (Quinolphos 2% EC), to freshwater Lamellibranch bivalve mollusc, Lamellidense corrianus during summer. Regression equation Y= -1.88 + 0.220 X 9% Fiducial limits, 0.0011 to 0.12 ppm. Calculated LC0= 0.01 ppm. 0 0.01 0.02 0.0 0.0 0.0 9 hr acute toxicity exposure of Ekalux (Quinolphos 2% EC), to freshwater Lamellibranch bivalve mollusc, Lamellidense corrianus during summer. Graph 2 Regression equation Y= -1.99 +.0228 X 9% Fiducial limits, 0.002 to 0.012 ppm. Calculated LC0= 0.008 ppm. 0 0.00 0.01 0.01 0.02 0.02 0.0 0.0 0.0