Ha. Anderson et al., PROFILES OF GREAT-LAKES CRITICAL POLLUTANTS - A SENTINEL ANALYSIS OF HUMAN BLOOD AND URINE, Environmental health perspectives, 106(5), 1998, pp. 279-289
To determine the contaminants that should be studied further in the su
bsequent population-based study, a profile of Great Lakes (GL) spore f
ish contaminant residues were studied in human blood and urine specime
ns from 32 sport fish consumers from three Great Laces: Lake Michigan
(n =10), Lake Huron (n = 11), and Lake Erie (n = 11). Serum was analyz
ed for 8 polychlorinated dioxin congeners, 10 polychlorinated furan co
ngeners, 4 coplanar and 32 other polychlorinated biphenyl (PCB) congen
ers, and 11 persistent chlorinated pesticides. Whole blood was analyze
d for mercury and lead. Urine samples were analyzed for 10 nonpersiste
nt pesticides (or their metabolites) and 5 metals. One individual was
excluded from statistical analysis because of an unusual exposure to s
elected analytes. Overall, the sample (n = 31) consumed, on average, 4
9 GL sport fish meals per year for a mean of 33 years. On average, the
general population in the GL basin consume 6 meals of GL sport fish p
er year. The mean tissue levels of most persistent, bioaccumulative co
mpounds also found in GL sport fish ranged from less than a twofold in
crease to that of PCB 126, which was eight times the selected backgrou
nd levels found in the general population. The overall mean coral toxi
c equivalent for dioxins, furans, and coplanar PCBs were greater than
selected background levels in the general population (dioxins, 1.8 tim
es; furans, 2.4 times; and coplanar PCBs, 9.6 times). The nonpersisten
t pesticides and most metals were nor identified in unusual concentrat
ions. A contaminant pattern among lake subgroups was evident. Lake Eri
e spore fish consumers had consistently lo,ver contaminant concentrati
ons than consumers of sport fish from Lakes Michigan and Huron. These
interlake differences are consistent. with contaminant patterns seen i
n sport fish tissue from the respective lakes; GL sport Bh consumption
was the most likely explanation for observed contaminant level among
this sample. Frequent consumers of sport fish proved to be effective s
entinels for identifying sport fish contaminants of concern. In the la
rger study to follow, serum samples will be tested for PCBs (congener
specific and coplanar), DDE, dioxin, and furans.