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Study methods, including recruitment and data collection protocols, laboratory analysis methods, and substitution methods for toxicant levels below the laboratory minimum detection limits, are briefly described here [for greater detail, see Schell et al. (2003)].
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Most of the routine methods for determining toxicant yields involve smoking cigarettes on machines that valve off the end of the cigarette between puffs (but the cigarettes continue to smoulder) [ 3, 14].
Many methods for environmental toxicants require an entire fully filled DBS for testing.
Values below the method detection limits for lead, mercury, PCBs, and HCB were imputed using the U.S. Environmental Protection Agency recommended method (U.S. EPA 1998) for toxicants with rates of detection of ≥ 50%.
Since the year 2000, Japanese medaka became the most favorable species for toxicant application via microinjection [20] [28].
As with control of arthropod pests of vertebrates, control of rodents with toxicants is failing mainly because of selection for toxicant resistance.
This is particularly evident for toxicant transporters, as well as for protein families detoxifying metals.
The underrepresentation is particularly evident for toxicant transporters and proteins involved in detoxifying metals.
Here we identified the mechanism of effect culmination for toxicant stress.
Cytosolic Ca2+ levels are abnormal in cells exposed to toxicants and understanding how these levels become altered may improve our ability to design high-throughput methods for the sensitive detection of cellular responses to a toxic exposure.
Most studies on interactions between toxicants and natural factors, including those completed in the EU project NoMiracle (Novel Methods for Integrated Risk Assessment of Cumulative Stressors in Europe) described herein, showed that effects of toxic chemicals on organisms can differ vastly depending purely on external conditions.
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