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. 2012 May;13(6):1004–1060. doi: 10.2174/138920112800399257

Table 2.

Ecotoxicity of Abamectin (ABM) to Aquatic and Terrestrial Organisms (for key to Dosages see Table Footnote)

Source Reference Test Organism Toxicity / response Conditions
VERTEBRATES
Wislocki et al. (1989) [120] Cyprinodon variegates (Sheepshead minnow) LC50 (96 h ) = 15 µg kg-1 Route of exposure to test organisms: dissolved state
Wislocki et al. (1989) [120] Ictalurus punctatus (Channel catfish) LC50 (96 h ) = 24 µg kg-1 Route of exposure: dissolved state
Wislocki et al. (1989) [120] Cyprinus spp. LC50 (96 h ) = 42 µg kg-1 Route of exposure: dissolved state
Tišler & Eržen (2006) [118] Danio rerio (Zebrafish) Mortality (LC):
96 h LC10 = 30.8 µg L-1
96 h LC50 = 55.1 µg L-1 (46.1–66.7 µg.L-1)
96 h LC90 = 98.3 µg L-1
Swimming ability (EC):
96 h EC50 = 21.1 µg L-1
96 h EC50 = 49.3 µg L-1 (37.3–63.3 µg L-1)
96 h EC90 = 114.8 µg L-1
Acute toxicity; exposure: semi-static, duration 96 h
Endpoints: mortality and swimming ability
TERRESTRIAL INVERTEBRATES
Ridsdill-Smith (1988) [157] Onthophagus binodis (dung beetle) Reduced larval survival and oviposition for 4-8 weeks post-treatment Injectable (cattle)
Dadour et al. (2000) [160] Onthophagus binodis (dung beetle) Reduced survival of newly emerged beetles in dung voided 3-6 days post-treatment. Inhibition of egg laying in dung voided 5-6 wks previously Injectable (cattle); Sub-lethal effects
Houlding et al. (1991) [159] Onthophagus binodis (dung beetle) Reduced survival of newly emerged beetles in dung voided 3-6 days post-treatment; delayed oocyte development Injectable (cattle)
Doherty et al. (1994) [66] Digitonthophagus gazella (dung beetle) Oviposition not reduced; complete mortality of larvae with ≥ 16µg a.i. kg-1 Injectable 1% formulation (cattle)
Wardhaugh & Mahon (1991) [155] Onthophagus spp.; Euoniticellus fulvus (dung beetles) Dung of ABM-treated cattle attracted more dung beetles than dung voided by untreated animals Injectable (cattle)
Youn et al. (2003) [139] Harmonia axyridis (Asian ladybird beetle) LC50 (eggs) <0.09 mg a.i. L-1
LC50 (1st instar) <0.09 mg a.i. L-1
LC50 (2nd instar) <0.09 mg a.i. L-1
LC50 (3rd instar) <0.09 mg a.i. L-1
LC50 (4th instar) = 18.40 mg a.i. L-1
LC50 (pupae) <0.09 mg a.i. L-1
LC50 (4th instar) = 4.90 mg a.i. L-1
Mortality 48 h (mobile stages)
eggs and pupae: one week
Ahmad et al. (2008) [144] Spodoptera litura (Noctuidae) LC50 =18.5 - 2342 mg L-1 Mortality assessed after 72 h exposure to ABM. Comparison laboratory susceptible population with field populations
Wang et al. (2008) [135] Anagrus nilaparvata (Hymenoptera Mymaridae) LC50 = 8.5 mg a.i. L-1 1 h exposure (contact); emulsible concentrate 1% a.i.; final test concentration: 16 mg a.i. L-1
Guglielmone et al. (1999) [154] Haematobia irritans (Horn fly) 100% mortality in dung voided 7 days post-treatment Injectable (cattle) egg-adult development
Clarke & Ridsdill-Smith (1990) [158] Musca vetustissima (Bush fly) Reduced survival and enhanced asymmetry of wing veins for flies from dung voided 4 weeks post injection; no effect on survival or asymmetry at weeks 8 to 11 Injectable (cattle) egg-adult development
Ridsdill-Smith (1988) [157] Musca vetustissima (Bush fly) 0% egg-adult survival in dung voided up to 2 wks post-treatment 98% survival by wk 8 Injectable (cattle)
Wardhaugh & Mahon (1991) [155] Musca vetustissima (Bush fly) 0% larval survival days 3-25. 6 % at day 35 Injectable (cattle)
Wardhaugh & Mahon (1998) [156] Musca vetustissima (Bush fly) Fly survival suppressed for 16-32 days Injectable (cattle)
Kolar et al. (2008) [146] Folsomia candida (springtail) LC50 (survival) = 67 mg kg-1 d.s.
EC50 (reproduction) = 5.2 mg kg-1 d.s.
EC50 (reproduction) = 13 mg kg-1 d.s.
Soil; mortality, reproduction after 28 days of exposure
Kolar et al. (2008) [146] Folsomia candida (springtail) LC50 (survival) = 1.0 mg kg-1 d.f.
NOEC (reproduction) = 0.8 mg kg-1 d.f.
EC50 (reproduction) = 1.4 mg kg-1 d.f.
Concentrations of ABM in sheep faeces; mortality, reproduction after 28 days of exposure
Diao et al. (2007) [145] Folsomia candida (springtail) NOEC (survival) >2.5 mg kg-1 dry weight
LOEC (survival) >2.5 mg .kg-1 d.w.
EC50 (survival) >2.5 mg kg-1 d.w.
EC50 (survival) >2.5 mg kg-1 d.w.
NOEC (reproduction) = 0.25 mg kg-1 d.w.
LOEC (reproduction) = 0.50 mg kg-1 d.w.
EC50 (reproduction) = 0.19 mg kg-1 d.w.
EC50 (reproduction) = 0.68 mg kg-1 d.w.
21 days exposure in soil; mortality, reproduction
Diao et al. (2007) [145] Folsomia fimetaria (springtail) LOEC (survival) =1.00 mg kg-1 d.w.
EC50 (survival) = 0.48 mg kg-1 d.w.
EC50 (survival) = 0.81 mg kg-1 d.w.
NOEC (reproduction) <0.25 mg kg-1 d.w.
LOEC (reproduction) = 0.25 mg kg-1 d.w.
EC50 (reproduction) = 0.05 mg kg-1 d.w.
EC50 (reproduction) = 0.33 mg kg-1 d.w.
21 days exposure in soil; mortality, reproduction
Umina et al. (2010) [134] Sminthurus viridis (Collembolan, Lucerne flea) LD50 = 18.94 mg L-1 a.i. = 18 g L-1; dilution 300 ml 50 L-1 water ; contact 8h; mortality
Lin et al. (2009) [94] Tetranychus cinnabarinus (Acariformes, Tetranychidae) F0 LC50 = 0.02 mg L-1
F0 LC90 = 0.04 mg L-1
F42 LC50 = 0.15 mg L-1
F42 LC90 = 0.39 mg L-1
Selection of resistance to ABM in Tetranychus cinnabarinus (generations F0 to F42). Mortality 24h
Umina et al. (2010) [134] Halotydeus destructor (redlegged earth mite) LD50 = 97 mg L-1 a.i. = 18 g L-1; dilution 300 ml.50 L-1 water; contact 8h; mortality
Umina et al. (2010) [134] Penthaleus falcatus (blue oat mite) LD50 = 30 mg L-1 a.i. = 18 g L-1; dilution 300 mL 50 L-1 water; contact 8h; mortality
Umina et al. (2010) [134] Bryobia sp. (clover mite) LD50 = 155 mg L-1 a.i. = 18 g L-1; dilution 300 mL 50 L-1 water; contact 8h; mortality
Lin et al. (2009) [94] Tetranychus cinnabarinus (Acariformes, Tetranychidae) F0 LC50 = 0.02 mg L-1
F0 LC90 = 0.04 mg L-1
F42 LC50 = 0.15 mg L-1
F42 LC90 = 0.39 mg L-1
Selection of resistance to ABM in Tetranychus cinnabarinus (generations F0 to F42). Mortality 24h
Kolar et al. (2008) [146] Porcellio scaber (isopod) LC50 (survival) = 69 mg kg-1 d.s. Soil; mortality after 21 days of exposure
Wislocki et al. (1989) [120] Eisenia fetida (compost earthworm) LC50 = 28 mg kg-1 d.w. After 28 days exposure
Jensen et al. (2007) [153] Eisenia fetida (compost earthworm) EC50 = 0.06 mg kg-1: Change in biomass.
LOEC for cocoon production: 0.25 mg kg-1
EC50 and EC50 approximately 0.16 and 1.03 mg kg-1 for cocoon production
No cocoons production at concentration 5 mg kg-1
E. fetida were exposed to 0, 0.25, 0.5, 1, 1.5, 2.5 and 5 mg kg-1 d.s.
Kolar et al. (2008) [146] Eisenia andrei (earthworm) LC50 (survival) = 18 mg kg-1 d.s.
LOEC (weight loss) = 29 mg kg-1 d.s.
NOEC (weight loss) = 9.8 mg kg-1 d.s.
Soil; mortality, weight loss after 28 days of exposure
Kolar et al. (2008) [146] Eisenia andrei (earthworm) LC50 (survival) >1.4 mg kg-1 d.f.
no effect on reproduction
NOEC > 1.4 mg kg-1 d.f.
Sheep faeces; mortality, reproduction after 28 days of exposure
Diao et al. (2007) [145] Eisenia andrei (earthworm) NOEC (survival) = 5.0 mg kg-1 d.s.
LOEC (survival) >5.0 mg kg-1 soil wt
EC50 (survival) >5.0 mg kg-1 soil wt
EC50 (survival) >5.0 mg kg-1 soil wt
NOEC (reproduction) < 0.25 mg kg-1 soil wt
Soil; mortality, reproduction after 70 days of exposure
Sun et al. (2005) [206] Eisenia fetida (earthworm) LC50 (7 days) = 24 mg kg_1 (d.w.)
LC50 (14 days) = 17 mg kg_1 (d.w.)
After 14 days of exposure in artificial OECD soil
Kolar et al. (2008) [146] Enchytraeus crypticus (enchytraeid) EC50 (survival) = 111 mg kg-1 d.s.
EC50 (reproduction) = 4.6 mg kg-1 d.s.
EC50 (reproduction) = 38 mg kg-1 d.s.
Soil; mortality, reproduction after 28 days of exposure
Kolar et al. (2008) [146] Enchytraeus crypticus (enchytraeid) LC50 (survival) = 1.1 mg kg-1 d.f.
EC50 (reproduction) = 0.9 mg kg-1 d.f.
NOEC = 0.8 mg kg-1 d.f.
Concentrations of ABM in sheep faeces; mortality, reproduction after 28 days of exposure
Diao et al. (2007) [145] Enchytraeus crypticus (enchytraeid) NOEC (survival) = 10 mg kg-1 d.s.
LOEC (survival) = 150 mg kg-1 d.s.
EC50 (survival) = 78 mg kg-1 d.s.
NOEC (reproduction) = 10 mg kg-1 d.s.
LOEC (reproduction) = 25 mg kg-1 d.s.
EC50 (reproduction) = 12 mg kg-1 d.s.
EC50 (reproduction) = 24 mg kg-1 d.s.
21 days exposure in soil; mortality, reproduction
Aquatic Invertebrates
Wislocki et al. (1989) [120] Penaeus duorarum (Decapoda) 96 h LC50 = 1.6 µg kg-1 Route of exposure: dissolved state; 96 h exposure
Wislocki et al. (1989) [120] Callinectes sapidus (Blue crab, Decapoda) 96 h LC50 = 153 µg kg-1 Route of exposure: dissolved state; 96 h exposure
Wislocki et al. (1989) [120] Daphnia magna (Cladocera) 48 h LC50 = 0.34 µg kg-1 Route of exposure: dissolved state; 24 h exposure
Tišler & Eržen (2006) [118] Daphnia magna (Cladocera) 24 h EC50 = 0.11 µg L-1
48 h EC50 = 0.12 µg L-1
24 h EC50 = 0.33 µg L-1 (range 0.21–0.43 µg.L-1)
48 h EC50 = 0.25 µg L-1 (range 0.21–0.30 µg.L-1)
24 h EC90 = 0.97 µg L-1
48 h EC90 = 0.50 µg L-1
Acute toxicity. Exposure: static; duration 24 and 48 h
Endpoint: immobility
Tišler & Eržen (2006) [118] Daphnia magna (Cladocera) 21 d LOEC = 0.009 µg L-1
21 d NOEC = 0.005 µg L-1
21 d IC25 = 0.007 µg L-1
Chronic toxicity.
Wislocki et al. (1989) [120] Neomysis bahia (Mysidacea) 96 h LC50 = 0.022 µg kg-1 Route of exposure: dissolved state; 96 h exposure
Wislocki et al. (1989) [120] Crassostrea virginica (Bivalvia) 96 h LC50 = 430 µg kg-1 Route of exposure to test organisms: dissolved state; 96 h exposure
ALGAE
Tišler & Eržen (2006) [118] Scenedesmus subspicatus no growth inhibition at 10 µg L-1 ABM
72 h EC50 = 0.7 mg L-1
72 h EC50 = 4.4 mg L-1
72 h EC90 = 21 mg L-1
Exposure: static; chronic toxicity
MICRO-ORGANISMS
Tišler & Eržen (2006) [118] Vibrio fischeri (luminescent bacteria) 30 min EC20 = 390 µg L-1
30 min EC50 = 690 µg L-1 (610-770 µg L-1)
30 min EC80 = 1200 µg L-1
Exposition (static) 30 min to ABM; endpoint: luminescence

Dosages for cattle are: 500 (pour-on), 200 (injectable) or 200 (oral) µg kg-1 b.w.