Lj. Blus et al., CLARIFICATION OF EFFECTS OF DDE ON SHELL THICKNESS, SIZE, MASS, AND SHAPE OF AVIAN EGGS, Environmental pollution, 95(1), 1997, pp. 67-74
Moriarty et al. (1986) used field data to conclude that DDE decreased
the size or altered the shape of avian eggs; therefore, they postulate
d that decreased eggshell thickness was a secondary effect because, as
a general rule, thickness and egg size are positively correlated. To
further test this relationship, the present authors analysed data from
eggs of captive American kestrels. Falco sparverius given DDT- or DDE
-contaminated or clean diets and from wild brown pelicans Pelecanus oc
cidentalis collected both before (pre-1946) and after (post-1945) DDT
was introduced into the environment. Pertinent data from other field a
nd laboratory studies were also summarized. DDE was not related to and
did not affect size, mass, or shape of eggs of the brown pelican or A
merican kestrel; but the relationship of DDE to eggshell thinning held
true, Size and shape bf eggs of brown pelicans from the post-1945 era
and those of kestrels, on DDT-contaminated diets showed some signific
ant, but inconsistent, changes compared to brown pelican data from the
pre-1946 era or kestrels on clean diets, In contrast, nearly all samp
les of eggs of experimental kestrels given DDT-contaminated diets and
those of wild brown pelicans from the post-1945 era exhibited signific
ant eggshell thinning, Pertinent experimental studies with other sensi
tive avian species indicated no effects of DDE on the size or shape of
eggs, even though the high dietary concentrations caused extreme eggs
hell thinning and mortality of some adult mallards (Anas platyrhynchos
) in one study. These findings essentially controvert the argument tha
t decreased eggshell thickness is a secondary effect resulting from th
e primary effect of DDE-induced changes in the size or shape of eggs.