Dietary accumulation and quantitative structure-activity relationships fordepuration and biotransformation of short (C-10), medium (C-14), and long (C-18) carbon-chain polychlorinated alkanes by juvenile rainbow trout (Oncorhynchus mykiss)
At. Fisk et al., Dietary accumulation and quantitative structure-activity relationships fordepuration and biotransformation of short (C-10), medium (C-14), and long (C-18) carbon-chain polychlorinated alkanes by juvenile rainbow trout (Oncorhynchus mykiss), ENV TOX CH, 19(6), 2000, pp. 1508-1516
Juvenile rainbow trout (Oncorhynchus mykiss) were exposed to three [C-14]-p
olychlorinated alkanes (PCAs) (C10H15.3Cl6.7 C14H23.3Cl6.7, and C18H31.4Cl6
.6) at nominal concentrations of 1.5 and 15 mu g/g for 40 d, followed by 16
0 d of clean food, to measure bioaccumulation parameters and biotransformat
ion. These PCAs are identical in carbon-chain length and chlorine content t
o industrial chlorinated paraffin products, although their method of synthe
sis differs from that of chlorinated paraffin products. Half-lives ranged f
rom 26 to 91 d, biomagnification factors ranged from 0.9 to 2.8, and both e
xhibited increasing trends with increasing carbon-chain length. Data from t
his work and others on PCAs were used to determine biotransformation rates
and to examine quantitative structure-activity relationships for bioaccumul
ation and biotransformation. Quantitative structure-activity relationships
developed for half-life and biomagnification factor showed positive linear
relationships with the number of carbon atoms, of chlorine atoms, of total
carbon and chlorine atoms, and log K-ow. The PCA biotransformation rates (p
er day) ranged from -0.00028 to 8.4 and exhibited negative relationships wi
th the number of carbon atoms, of chlorine atoms, of total carbon and chlor
ine atoms, and log K-ow. Results suggest that PCAs with a total number of c
arbon and chlorine atoms between 22 and 30 are slowly, or are not, biotrans
formed in juvenile rainbow trout. Increasing carbon-chain length and chlori
ne content result in greater bioaccumulation of PCAs by reducing partition-
based (i.e., diffusion) and metabolic (i.e., biotransformation) elimination
processes. High bioaccumulation potential and low biotransformation rates
of medium (C14-18) and long (C18-30) carbon-chain PCAs and highly chlorinat
ed PCAs indicate that information is needed regarding the environmental con
centrations of these PCAs in aquatic food chains.