Table 2. Average number ± S.E. (total number) of non-target organisms collected with the area sampler or emergence traps.
Taxon | Organism | Pre-application | First-application | Second-application | |||
Control | Treatment | Control | Treatment | Control | Treatment | ||
Ephemeroptera | Mayfly nymphs | 1.08±0.18 (523) | 1.33±0.18 (501) | 0.98±0.16 (159) | 1.28±0.17 (207) | 1.30±0.21 (216) | 1.15±0.17 (187) |
Mayfly (pre-) adults | 0.94±0.19 (174) | 2.25±0.33 (418)*** | 0.10±0.04 (11) | 0.77±0.16 (83) *** | 0.27±0.04 (30) | 0.27±0.11 (34) | |
Odonata | |||||||
Zygoptera | Damselfly nymphs | 0.06±0.01 (28) | 0.04±0.02 (20) | 0.42±0.13 (68) | 0.35±0.06 (56) | 0.73±0.15 (115) | 0.60±0.09 (97) |
Damselfly adults | 0.20±0.06 (76) | 0.17±0.49 (68) | 0.03±0.16 (3) | 0.02±0.13 (2)a | 0.24±0.06 (39) | 0.34±0.14 (56) | |
Anisoptera | Dragonfly nymphs | 0.15±0.03 (55) | 0.16±0.02 (60) | 0.18±0.04 (29) | 0.22±0.037 (35) | 0.44±0.06 (68) | 0.57±0.08 (93) |
Heteroptera | |||||||
Veliidae | Broad shouldered water strider | 0.19±0.04 (73) | 0.13±0.02 (49) | 0.62±0.12 (100) | 0.46±0.22 (75) | 0.04±0.02 (7) | 0.01±0.01 (1)a |
Nepidae | Water scorpion | 0.01±0.02 (5) | 0.04±0.02 (8) | 0.07±0.02 (12) | 0.06±0.02 (10) | 0.06±0.20 (9) | 0.06±0.35 (10) |
Corixidae | Water boatmen | 1.32±0.21 (500) | 0.59±0.93 (223)* | 1.31±0.12 (213) | 1.20±0.11 (195) | 0.02±0.01 (3) | 0.01±0.01 (2)a |
Notonectidae | Back swimmers | 0.59±0.76 (222) | 0.79±0.11 (300) | 0.83±0.11 (135) | 0.79±0.13 (128) | 0.77±0.15 (124) | 0.30±0.05 (49)** |
Coleoptera | Water beetles | 13.89±1.32 (5187) | 13.99±1.89 (5279) | 3.43±0.46 (556) | 3.76± 0.23 (610) | 0.01± 0.01 (2) | 0.03±0.01(5)a |
Diptera | |||||||
Brachycera | House flies, biting flies | 0.16±0.03 (30) | 0.15±0.03 (27) | 0.01±0.01 (1) | 0.06±0.01 (6)a | 0.03±0.01 (3) | 0 (0)a |
Hymenoptera | |||||||
Apocrita | Wasp | 0.02±0.01 (4) | 0.01±0.009 (1)a | 0.93±0.12 (151) | 0.85±0.11 (138) | 0.01±0.01 (2) | 0.04±0.01 (7)a |
Arachnida | |||||||
Hydrachnellae | Water mite | 0.25±0.03 (93) | 0.13±0.02 (51)* | 0.07±0.02 (12) | 0.11±0.70 (18) | 0.01±0.01 (2) | 0.02±0.01 (4)a |
Molluscs | Snails | 0.21±0.04 (57) | 0.29±0.04 (87) | 0.03±0.01 (3) | 0.04±0.01 (4)a | 0.12±0.69 (21) | 0.14±0.01 (23) |
Annelids | |||||||
Hirudinea | Leech | 0.01±0.01 (1) | 0.01±0.01 (1)a | 0.10±0.12 (17) | 0.12±0.11 (20) | 0.01±0.01 (2) | 0.01±0.01 (2)a |
Fish | Tilapia, mudfish | 0.01±0.01 (5) | 0 (0) a | 0.14±0.10 (22) | 0.06±0.02 (10) | 0.25±0.06 (41) | 0.19±0.07 (30) |
Amphibian | Tadpoles | 0.69±0.26 (261) | 0.45±0.06 (171) | 0.75±0.16 (121) | 1.41±0.20 (229) ** | 0.54±0.09 (88) | 0.67±0.11 (109) |
Frogs | 0.03±0.02 (7) | 0.01±0.05 (3) | 0.06±0.03 (11) | 0.03±0.01 (6) | 0.02±0.01 (2) | 0 (0)a |
a.sample size too small for analysis.
Average number ± S.E. (total number) of non-target organisms collected with the area sampler or emergence traps before and after the first and second Aquatain application. The numbers of each non-target organism in the control and treatment paddies, before and after the first and second Aquatain application, was compared by generalized estimating equations (n.s., no significant difference; *, p<0.05; **, p<0.01; ***, p<0.001).