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However, Adamson et al., 2013 [24] observed differences in the positions of the linear exposure module, whereas this study did not.
Regional deposition analysis within the linear exposure chamber showed no statistical difference in deposited mass across the chamber at any airflows tested.
In addition to assessing total deposited mass across the dilution airflow range, a four QCM approach enabled the assessment of particulate deposition across the linear exposure module at all airflows tested (0.5 4.0 L/min).
Regional smoke deposition across the linear exposure module showed no statistical difference at any of the airflows tested (0.5-4.0 0.5-4.0 demonstrating uniform deposition within the chamber at aL/minsitions within this system.
We also ran trend analyses using a linear exposure term.
Assuming a linear exposure response function leads to overestimation of the impact of peak exposures.
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This is appropriate if there is a simple linear exposure-response relationship.
There was no significant departure from a linear exposure-response relationship (p>0.05).
Wald tests for a log linear exposure-response trend were based on the continuous estimates of crop density.
The associations between particulate pollution and daily mortality were not significantly different from a linear exposure-response relationship that extends throughout the full observed range of pollution.
The assumption of linear exposure-response was assessed graphically and by fitting alternative models with flexible spline functions and was found to be adequate.
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