Figure 1.

Comparison of profiles of chemicals with any vs. active vs. unknown designations for select pairs of assay end points and chemical classes, using Tox21 high-throughput screening data (Table 2) (Huang et al. 2016). (A) OPEs and androgen receptor antagonism, (B) PBDEs and estrogen receptor agonism, and (C) PBDEs and thyroid hormone receptor antagonism. Values below the limit of detection were replaced with half the limit. Unlabeled stacked bars represent chemicals that did not make appreciable contributions () to the geometric mean concentrations of that chemical class. Note: BDE-47, decabromodiphenyl ether–47; BDE-99, decabromodiphenyl ether–99; BDE-209, decabromodiphenyl ether–209; BDP, bisphenol A bis(diphenylphosphate); CDPP, cresyl di phenyl phosphate; EHDPP, 2-ethylhexyl diphenyl phosphate; OPEs, organophosphate esters; PBDEs, polybrominated diphenyl ethers; RDP, resorcinol bis(diphenyl phosphate); TBOEP, tris(2-butoxyethyl) phosphate; TCIPP, tris (1-chloro-2-propyl) phosphate; TDCIPP, tris(1,3-dichloro-2-propyl) phosphate; TMPP, tris(2,4,6-trimethoxyphenyl)phosphine; TPHP, triphenyl phosphate; TPP, triphenylphosphine; V6, 2,2-bis(chloromethyl)trimethylene bis(bis(2-chloroethyl)phosphate).