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Bisphenol A Environmental Exposure in Aquatic Ecosystems
Bisphenol A does not accumulate in aquatic organisms
to any appreciable extent and is not classified as bioaccumulative
by the U.S. Environmental Protection Agency. In tests
of 42-days duration, measured ratios of BPA in fish
to that in the surrounding water (bioconcentration factors)
range from 5.1 to 68 (Staples et al, 1998). In a freshwater
clam, bioconcentration factors in the range of 110-144
were measured at low temperatures (Heinonen et al, 2002).
Bioconcentration factors less than 100 are considered
to indicate a low potential for bioaccumulation. A bioconcentration
factor of 1000 has been considered a threshold for concern,
while factors greater than 5000 suggest that a substance
is persistent in the environment.
Acute toxicity levels for BPA, defined as the concentration
at which half of the organisms survive (LC50 values),
have been measured in a variety of aquatic organisms,
including freshwater and saltwater algae, invertebrates
(daphnids and mysid shrimp) and fish. LC50 values range
from 1000 to 20,000 micrograms/L (Staples et al, 1998;
Staples et al, 2002).
The No-Observed-Effect-Concentration (NOEC) of BPA
in a 21-day chronic reproduction test in Daphnia was
3160 microgram/L (Caspers, 1998). Effect concentrations
at the 10% level (EC10) were determined for both freshwater
and marine algae to be 1360 to 1680 micrograms/L and
400 to 690 micrograms/L, respectively (Alexander et
al, 1988).
The results of a multi-generation study on fathead
minnows showed that survival, growth and reproductive
fitness for three generations were affected only at
concentrations of 640 micrograms/L and higher, with
hatchability of F2 (second generation) eggs slightly
reduced at 160 micrograms/L. The NOEC measured in this
study was 16 micrograms/L. (Sohoni et al, 2001; Caunter,
2000).
A weight-of-evidence analysis of the aquatic hazards
posed by BPA was conducted with a focus on validated
studies and the ecologically relevant endpoints of survival,
growth and reproductive fitness. This analysis included
the use of statistical extrapolation techniques to assess
the full database of reported effect concentrations.
The study concludes that no adverse aquatic effects
are expected at concentrations below 100 micrograms/L
of BPA (Staples et al, 2002).
Comparison of this no-adverse-effect level for BPA
of 100 micrograms/L, which was deemed protective of
the structure and function of aquatic ecosystems, with
typically measured values in surface waters of 0.001
to 1.0 micrograms/L indicates that aquatic ecosystems
are unlikely to be adversely impacted by BPA (Staples
et al, 2002).
The data in the validated studies and reviews described
above, combined with current scientific understanding
of BPA toxicity, indicate that the current manufacturing
and use patterns of BPA pose virtually no risk to the
environment.


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