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. Author manuscript; available in PMC: 2019 Jul 1.
Published in final edited form as: Aquat Toxicol. 2018 Apr 21;200:1–12. doi: 10.1016/j.aquatox.2018.04.009

Table 1.

EC50 and LC50 values (168 hpf, with the exception of PTU 120 hpf), as well as the p-values indicating significant differences between LC50 and EC50 values, after exposure experiments (six concentrations per compound, 40 embryos per condition) at UA (effects on posterior chamber inflation).

Compound EC50 (mg/L) LC50 (mg/L) p-value Observed impaired posterior chamber inflationa Concentration at which effect on posterior chamber surface area (120 hpf) occursb
PTU 259 555.9 <0.0001 X EC50
IOP 2.791 3.471 0.0448 X No data
PFOA 108.5 362.5 0.0150 X EC10, EC30, EC50
BPA 4.7 8 0.0427 X EC10, EC30, EC50
BP2 10.55 15.48 <0.0001 X No data
TBP 0..42 0.84 <0.0001 X EC10, EC30, EC50
SA 82.6 137.3 <0.0001 X EC10, EC30, EC50
PFOS (Hagenaars et al., 2016) 2.12 8.35 <0.0001 X No data
ANS 112.2 124.7 0.0606 EC10, EC30, EC50
TCBPA 0.43 0.41 0.0687 No data
NaPER 3435 2952.7 <0.0001 No effect
MMI 772.0 894.8 0.1395 EC10, EC30, EC50
*No effect at 168 hpf
PFBS 830.3 921.9 0.3171 No effect
MBT (Stinckens et al., 2016) 3.2 4.2 0.1529 No effect
a

Observed effects on binary scoring of the absence of posterior chamber inflation (X = effect = significant difference between EC50 and LC50 values, UA) are given. Based on the exposure experiments at UA, EC10, EC30 and EC50 values were determined at 120 hpf and used to perform exposure experiments at UCR (three concentrations per compound, at least 40 embryos per condition, effects on posterior surface area).

b

Observed effects on posterior surface area (effect concentration, UCR, see section 3.2.2) are given.