M. Machala et al., Aryl hydrocarbon receptor-mediated activity of mutagenic polycyclic aromatic hydrocarbons determined using in vitro reporter gene assay, MUT RES-GTE, 497(1-2), 2001, pp. 49-62
Citations number
32
Categorie Soggetti
Molecular Biology & Genetics
Journal title
MUTATION RESEARCH-GENETIC TOXICOLOGY AND ENVIRONMENTAL MUTAGENESIS
Activation of aryl hydrocarbon receptor (AhR) by 30 polycyclic aromatic hyd
rocarbons (PAHs) was determined in the chemical-activated luciferase expres
sion (CALUX) assay, using two exposure times (6 and 24 h), in order to refl
ect the metabolization of PAHs. AhR-inducing potencies of PAHs were express
ed as induction equivalency factors (IEFs) relative to benzo[a]pyrene and 2
,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). In 24h exposure assay, the highe
st IEFs were found for benzo[k]fluoranthene, dibenzo[a,h]anthracene and dib
enzo[a,k]fluoranthene (approximately three orders of magnitude lower than T
CDD) followed by dibenzo[a,j]anthracene, benzo[j]fluoranthene, indeno[1,2,3
-cd]pyrene, and naphtho[2,3-a]pyrene. The 6 h exposure to PAHs led to a sig
nificantly higher AhR-mediated activity than the 24 h exposure (generally b
y two orders of magnitude), probably due to the high rate of PAH metabolism
. The strongest AhR inducers showed IEFs approaching that of TCDD. Several
PAHs, including some strong mutagens, such as dibenzo[a,l]pyrene, cyclopent
a[cd]pyrene, and benzo[a]perylene, elicited only partial agonist activity.
Calculation of IEFs based on EC25 values and/or 6 h exposure data is sugges
ted as an alternative approach to estimation of toxic potencies of PAHs wit
h high metabolic rates and/or the weak AhR agonists. The IEFs, together wit
h the recently reported relative mutagenic potencies of PAHs [Mutat. Res. 3
71 (1996) 123; Mutat, Res. 446 (1999) 1] were combined with data on concent
rations of PAHs in extracts of model environmental samples (river sediments
) to calculate AhR-mediated induction equivalents and mutagenic equivalents
. The highest AhR-mediated induction equivalents were found for benzo[k]flu
oranthene and benzo[j]fluoranthene, followed by indeno[1,2,3-cd]pyrene, dib
enzo[a,h]anthracene, benzo[a]pyrene, dibenzo[a,j]anthracene, chrysene, and
benzo [b]fluoranthene. High mutagenic equivalents in the river sediments we
re found for benzo[a]pyrene, dibenzo[a,e]pyrene, and naphtho[2,3-a]pyrene a
nd to a lesser extent also for benzo[a] anthracene, benzo[b]fluoranthene, i
ndeno[1,2,3-cd]pyrene, benzo[j]fluoranthene, dibenzo[a,e]fluoranthene and d
ibenzo[a,i]pyrene. These data illustrate that AhR-mediated activity of PAHs
, including the highly mutagenic compounds, occurring in the environment bu
t not routinely monitored, could significantly contribute to their adverse
effects. (C) 2001 Elsevier Science B.V. All rights reserved.