Table 2.
Summary of effects in the coiling assay with 21–47 h old zebrafish (D. rerio) embryos exposed to neurotoxicants
Concentration | Mean burst duration (s)1 | Age (h) | Light phase a | Burst count per minute | Age (h) | Light phase a | Surface water concentration b | |
---|---|---|---|---|---|---|---|---|
Acrylamide | 1.3 mM | + + | 45 | D2 |
+ + + + + + |
42 43 44 |
D2 | < 5 µg/L (70.34 µM) |
2.1 mM | + + | 45 | D2 |
+ + + + + |
38–40 41 45 |
D2 | ||
Carbaryl | 14.9 µM | L |
– – – + + |
24 27 |
Various rivers, Spain: 1.23–6.48 µg/ml (6.11–32.20 µM; Picó et al. (1994)) | |||
29.8 µM | L |
+ + + |
24–27 28 |
|||||
37.3 µM | – | 24 | L |
– – – – – |
23 24 |
L | ||
All | ~ | 30–47 | L, D2 | ~ | 30–47 | L, D2 | ||
Hexachlorophene | All | ~ | 29–38 | L | ~ | 29–38 | L | Urban drainage area (Greenboro, USA): 4.0–25.8 µg/L upstream (10–60 nM), 3.2–44.3 µg/L downstream (8–110 nM), and 15.2–48.3 µg/L in bottom water (40–120 nM) |
Ibuprofen | 48.6 µM | – – | 30 | L |
– – – – – – – – |
36–37 38–39 40–47 |
L D2 D2 |
USA (various samples): < 0.1 µg/L (0.5 nM)b |
145.4 µM |
– – – – – |
24 30–47 |
L D2 |
– – – | 24–47 | L, D2 | USA (various samples): < 0.1 µg/L (0.5 nM); Various ground- and surface-water samples, UK: 2030 µg/L (126.77 µM; Spurgeon et al. (2022)) | |
Rotenone | 1.0 nM | – – – | 22 | D1 | – – – | 22 | D1 | |
10.1 nM | – | 21 | D1 | Various ground- and surface-water samples, UK: 2030 µg/L (126.77 µM; Spurgeon et al. (2022)) | ||||
All | ~ | 30–47 | L, D2 | ~ | 30–47 | L, D2 |
1Activity: – minor reduction (p: 0.05–0.01); – – intermediate reduction (p: 0.01–0.001); – – – strong reduction (p: ≤ 0.001); + minor increase (p: 0.05–0.01); + + intermediate increase (p: 0.01–0.001); + + + strong increase (p: ≤ 0.001); ~ hyperactivity that could not be statistically analysed
aLight phase: D1 – dark phase 1 until 13.5 h; L − light phase until 37.5 h; D2 − dark phase 2 until 47 h: bPubChem (where available, locations provided)