Combined toxicity effects of MTBE and pesticides
measured with Vibrio fischeri and Daphnia magna bioassays
M.D. Hernando, M. Ejerhoon, A.R. Fernandez-Alba, Y.
Chisti
This
article review is about the use of Vibrio
fischeri and Daphnia magna bioassays
as a tool to measure the combined toxicity effects of methyl-tert-butyl ether
(MTBE) and several components of pesticides Diuron, Linuron, Dichlofluanid, Sea
nine, Irgarol and tributyltin (TBT). MTBE is widely used as fuel oxygenate in
gasoline commonly contaminates aquatic ecosystem and has a low acute and
chronic toxicity when tested alone. However, combination of chemicals found in
aquatic environment affects the toxicity of the individual compounds. It can be
synergistic, additive or antagonistic effects. The study’s goal are to know the
combined effects of pesticides found in lake, marinas and river which were Diuron,
Dichlofluanid, Sea nine 211, Irgarol 1051, Linuron and Tributyltin (TBT) and
MTBE. V. fisheri and D. magna bioassay was used to evaluate
the toxicity level of MTBE and pesticide alone and together the combined
effects. They quantified the toxic effect using EC50.
They
also evaluated the time generated by the toxic response of V. fisheri and D. magna.
Chemical
were purchased and tested individually and as a combination. The compounds were
then evaluated using V. fisheri
bioassay and the light was evaluated using BiotoxtTM.. D. magna bioassay used DaphtoxkitTM
and was assessed by noting the motility of D. magna. The data were also converted into a Mixture Toxicity
Index. The EC50 was replicated six times for reproducibility.
Chemical analyses were also used to detect the disappearance of MTBE because it
is highly volatile, highly water soluble and a persistent pollutant.
MTBE is toxic to
invertebrates at concentrations of 57 to >1000 mg/L and the value of MTBE’s
toxicity on D. magna is EC50=720 mg/L and is consistent with the
reported 96-h EC50 measurement of 681 mg/L. As a result the typical
concentration of MTBE in environment does not harm aquatic life. Presence of
MTBE enhances the EC50 of Diuron, Dichlofluanid, TBT and Linuron and
while Sea nine and Irgarol were not raised.
For us, this study is
actually reliable for future studies as the result were able to answer their
objectives in terms of identifying the effect of the MTBE to the bioassays and
the time needed to take effect (in the results). The results obtained were all
consistent to the goal when the effects on the bioassays were clearly identified.
Even if the paper has no recommendations, we say, the results are reliable and
can be used as a reference for parallel studies.
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