Table 6.
Source | Reference | Test Organism | Toxicity / Response | Conditions |
---|---|---|---|---|
VERTEBRATES | ||||
McHenery & Mackie (1999), Schering-Plough Anim. Health (2002) | [246-247] | Oncorhynchus mykiss (Rainbow trout) | 96 h LC50 = 174 µg L-1 96 h NOEC = 48.7 µg L-1 |
|
Chukwudebe et al. (1996) | [257] | Lepomis macrochirus (Bluegill sunfish) | 96 h LC50 = 180 µg L-1 96 h NOEC = 87 µg L-1 |
|
McHenery & Mackie (1999), Schering-Plough Anim. Health (2002) | [246-247] | Pimephales promelas (Fathead minnow) | 96 h EC50 (adult) = 194 µg L-1 96 h NOEC (adult) = 156 µg L-1 96 h LC50 (MATC) = 18 µg L-1 96 h NOEC (MATC) = 12 µg L-1 96 h LOEC = 28 µg L-1 |
mortality (96 h); early life stages (96 h): MATC and LOEC |
McHenery & Mackie (1999);, Schering-Plough Anim. Health (2002) | [246-247] | Cyprinodon variegatus (Sheepshead minnow) | 96 h LC50 = 1,350 µg L-1 | exposition 96 h |
TERRESTRIAL INVERTEBRATES | ||||
Ahmad et al. (2008) | [144] | Spodoptera litura (Lepidoptera: Noctuidae) | 72 h LC50 = 0.03 (lab. pop.) - 2.31 mg L-1 | Mortality assessed after 72 h exposure to emamectin. Comparison laboratory susceptible population with field populations |
Argentine et al. (2002) | [256] | Spodoptera exigua (Lepidoptera) | 6 d LC50 = 0.026 mg L-1 6 d LC90 = 0.305 mg L-1 |
Mortality recorded 6 d after application (contact with treated plant) |
Argentine et al. (2002) | [256] | Spodoptera frugiperda (Lepidoptera) | 6 d LC50 = 0.003 mg L-1 6 d LC90 = 0.007 mg L-1 |
Mortality recorded 6 d after application (contact) |
Argentine et al. (2002) | [256] | Heliothis virescens (Lepidoptera) | 6 d LC50 = 0.003 mg L-1 6 d LC90 = 0.009 mg L-1 |
Mortality recorded 6 d after application (contact) |
Argentine et al. (2002) | [256] | Plutella xylostella (Lepidoptera) | 6 d LC50 = 0.001 mg L-1 6 d LC90 = 0.005 mg L-1 |
Mortality recorded 6 d after application (contact) |
Argentine et al. (2002) | [256] | Trichoplusia ni (Lepidoptera) | 6 d LC50 = 0.007 mg L-1 6 d LC90 = 0.013 mg L-1 |
Mortality recorded 6 d after application (contact) |
Argentine et al. (2002) | [256] | Pseudoplusia includens (Lepidoptera) | 6 d LC50 = 0.006 mg L-1 6 d LC90 = 0.022 mg L-1 |
Mortality recorded 6 d after application (contact) |
AQUATIC INVERTEBRATES | ||||
Waddy et al. (2007) | [255] | Homarus americanus (American lobster) | NOEL (moult cycle) = 0.12 mg a.i. g-1 lobster LOEL (moult cycle) = 0.22 mg a.i. g-1 lobster |
dose response of ovigerous lobsters to emamectin benzoate |
McHenery & Mackie (1999), Schering-Plough Anim. Health (2002) | [246-247] | Nephrops norvegicus (Decapoda) | 96 h LC50 = 983 µg L-1 192 h LC50 = 572 µg L-1 96 h NOEC = 814 µg L-1 192 h NOEC =440 µg L-1 96 h LC50 >68.2 mg kg-1 192 h LC50 >68.2 mg kg-1 96 h NOEC = 68.2 mg L-1 192 h NOEC = 68.2 mg kg-1 |
water exposure (96 h and 192 h) Feed exposure (96 h and 192 h) (concentration reported µg.kg-1feed) |
McHenery & Mackie (1999), Schering-Plough Anim. Health (2002) | [246-247] | Crangon crangon (Decapoda) | 96 h LC50 = 242 µg L-1 192 h LC50 = 161 µg L-1 96 h NOEC = 161 µg L-1 192 h NOEC = 161 < µg L-1 96 h LC50 >69.3 mg L-1 192 h LC50 >69.3 mg L-1 96 h NOEC = 69.3 mg L-1 192 h NOEC = 69.3 mg L-1 |
water exposure (96 h and 192 h) Feed exposure (96 h and 192 h) (concentration reported µg.kg-1 feed) |
Bravo et al. (2008) | [248] | Caligus rogercresseyi (Copepod) | EC50 = 57-203 µg L-1 (µg kg-1) (summer season) EC50 = 202-870 µg L-1 (µg kg-1) (winter season) EC50 (naive individuals) = 34 µg L-1 (µg kg-1) |
End point: immobilization; resistance in copepods exposed to emamectin benzoate |
Willis & Ling (2003) | [249] | Acartia clausi (Copepod) | 48 h EC50 (N6) = 0.57 µg L-1 96 h EC50 (N6) = 0.48 µg L-1 48 h EC50 (C1) = 0.28 µg L-1 96 h EC50 (C1) = 0.13 µg L-1 48 h EC50 (C6) = 0.29 µg L-1 96 h EC50 (C6) = 5.27 µg L-1 NOEC (adult) = 0.05 µg L-1 LOEC (adult) = 0.16 µg L-1 Egg production reduced for concentrations of 0.16 and 0.5 µg L-1 |
three life stages: nauplii (N6), copepodites (instars C1 and C6) and adults exposed 48 h and 96 h to emamectin benzoate Daily egg production after 96 h exposition |
McHenery & Mackie (1999), Schering-Plough Anim. Health (2002) | [246-247] | Artemia salina (Anostraca) | LC50 (6 h) = 1.73 mg L-1 | IC100 |
McHenery & Mackie (1999), Schering-Plough Anim. Health (2002) | [246-247] | Mysidopsis bahia (Mysidacea) | 96 h LC50 = 0.04 mg L-1 96 h NOEC = 0.02 µg L-1 |
|
Willis & Ling (2003) | [249] | Pseudocalanus elongatus (Copepod) | 48 h EC50 (N6) = 0.12 µg L-1 48 h EC50 (C1) = 0.14 µg L-1 96 h EC50 (C1) = 0.17 µg L-1 48 h EC50 (C6) = 0.45 µg L-1 96 h EC50 (C6) = 10.9 µg L-1 |
life stages: nauplii (N6) and copepodites (C1 and C6) exposed 48 h and 96 h to emamectin benzoate |
Willis & Ling (2003) | [249] | Temora longicornis (Copepod) | 48 h EC50 (N6) = 0.23 µg L-1 48 h EC50 (C1) = 0.41 µg L-1 48 h EC50 (C6) = 2.8 µg L-1 |
life stages: nauplii (N6) and copepodites (C1 and C6) exposed 48 h to emamectin benzoate |
Willis & Ling (2003) | [249] | Oithona similis (Copepod) | 48 h EC50 (N6) >15.8 µg L-1 96 h EC50 (N6) >15.8 µg L-1 48 h EC50 (C1) = 15.86 µg L-1 96 h EC50 (C1) = 14.8 µg L-1 48 h EC50 (C6) = 232 µg L-1 96 h EC50 (C6) = 113 µg L-1 |
life stages: nauplii (N6) and copepodites (C1 and C6) exposed 48 h and 96 h to emamectin benzoate |
McHenery & Mackie (1999), Schering-Plough Anim. Health (2002) | [246-247] | Corophium volutator (Amphipoda) (mud shrimp) | 10 d LC50 = 6.32 µg L-1 10 d NOEC = 3.2 µg L-1 10 d LC50 = 193 µg kg-1 10 d NOEC =115 µg kg-1 |
water (µg. L-1) sediment (µg.kg-1wet sediment) |
McHenery & Mackie (1999), Schering-Plough Anim. Health (2002) | [246-247] | Daphnia magna (Cladocera) | 48 h LC50 (48 h) = 1.0 µg L-1 48 h NOEC (48 h) = 0.3 µg L-1 21 d LC50 reprod. = 0.16 µg L-1 21 d NOEC reprod. = 0.09 µg L-1 21 d MATC = 0.12 µg L-1 21 d LC50 feed = 0.13 µg kg-1 |
mortality (48 h); reproduction - LOEC (21 d); MATC (maximum acceptable toxicant concentration)(21 d); LC50 (adults) feed exposure (21 d) (µg kg-1feed) |
McHenery & Mackie (1999), Schering-Plough Anim. Health (2002) | [246-247] | Capitella capitata (Polychaete worm, Capitellidae) | 21 d LC50 = 1.04 mg L-1 21 d NOEC = 460 µg L-1 |
Exposition 21 d |
McHenery & Mackie (1999), Schering-Plough Anim. Health (2002) | [246-247] | Arenicola marina (lugworm, Polychaeta) | 10 d LC50 = 111 µg kg-1 10 d NOEC = 56.0 µg kg-1 |
sediment (µg kg-1 wet sediment) |