The
discovery of the significant lethal impacts of the tire additive
transformation product N-(1,3-dimethylbutyl)-N′-phenyl-p-phenylenediamine quinone
(6PPD-Q) on coho salmon has garnered global attention. However, the
bioaccumulation and trophic transfer of tire additives and their transformation
products (TATPs) within food webs remain obscure. This study first
characterized the levels and compositions of 15 TATPs in the Pearl
River Estuary, estimated their bioaccumulation and trophic transfer
potential in 21 estuarine species, and identified priority contaminants.
Our observations indicated that TATPs were prevalent in the estuarine
environment. Eight, six, seven, and 10 TATPs were first quantified
in the shrimp, sea cucumber, snail, and fish samples, with total mean
levels of 45, 56, 64, and 67 ng/g (wet weight), respectively. N,N′-Diphenyl-p-phenylenediamine (DPPD) and N,N′-bis(2-methylphenyl)-1,4-benzenediamine (DTPD) exhibited
high bioaccumulation. Significant biodilution was only identified
for benzothiazole, while DPPD and DTPD displayed biomagnification
trends based on Monte Carlo simulations. The mechanisms of bioaccumulation
and trophodynamics of TATPs could be explained by their chemical hydrophobicity,
molecular mass, and metabolic rates. Based on a multicriteria scoring
technique, DPPD, DTPD, and 6PPD-Q were characterized as priority contaminants.
This work emphasizes the importance of biomonitoring, particularly
for specific hydrophobic tire additives.