Tw. Custer et al., CONTAMINANT CONCENTRATIONS AND BIOMARKER RESPONSE IN GREAT BLUE HERONEGGS FROM 10 COLONIES ON THE UPPER MISSISSIPPI RIVER, USA, Environmental toxicology and chemistry, 16(2), 1997, pp. 260-271
In 1993, great blue heron (Ardea herodias: GBH) eggs were collected fr
om 10 colonies on the upper Mississippi River (UMR). They were then ar
tificially incubated until pipping and analyzed for mercury, selenium,
and organochlorines. Livers of embryos were analyzed for hepatic micr
osomal ethoxyresorufin-O-dealkylase (EROD) activity and four measures
of oxidative stress. Brains were measured for asymmetry and blood was
measured for the coefficient of variation of DNA (DNA CV). Organochlor
ine concentrations were generally low (geometric mean DDE = 1.3 mu g/g
wet weight; polychlorinated biphenyl [PCB] = 3.0 mu g/g; 2,3,7,8-tetr
achlorodibenzo-p-dioxin [TCDD] = 11.5 pg/g). Eggshell thickness was ne
gatively correlated with DDE concentrations. Mercury (geometric mean =
0.8 mu g/g dry weight) and selenium (3.1 mu g/g dry weight) concentra
tions in GBH eggs were within background levels. EROD activity was not
correlated with total PCBs, TCDD, or toxic equivalents (TEQs), based
on the relative contribution of individual PCB congeners, dibenzodioxi
ns (PCDDs), and dibenzofurans (PCDFs) to total calculated TEQs. Three
of the four measures of oxidative stress were correlated with mercury
concentrations. Twenty of 43 (47%) embryo brains were asymmetrical and
the embryos with asymmetrical brains had higher EROD concentrations i
n the liver and higher DNA CV in the blood than embryos with symmetric
al brains.