Long-term exposure to traffic-related air pollutants (TRAPs) has been associated with multiple adverse health effects. However, many TRAPs, such as ultrafine particles, are poorly measured and thus their association with health outcomes is difficult to characterize. Our objective is to identify geographic characteristics that distinguish diurnal trends in TRAP concentrations at monitoring sites in order to estimate spatial contrasts in long-term average concentrations. Mobile monitoring (driving to many locations with multiple instruments) permits us to measure many TRAPs at many locations, but these measurements have short durations and may not capture the pollutant’s underlying trends. Therefore, these measurements may not reflect a site’s true long-term average due to our inability to fully sample the diurnal trend of the pollutant. In order to quantify the role of diurnal trends on annual averages, we use hourly measurements of CO, NO2, and PM2.5 from California Environmental Protection Agency’s (CalEPA) monitoring sites where the true long-term averages are known. Using Principal Component Analysis (PCA) to reduce the number of dimensions, we will regress the pollutant levels against the time of day, the physical covariates and their interaction terms. The geographical variables include, but are not limited to, distance to a highway, distance to bodies of water, Normalized Difference Vegetation Index (NDVI), and population density. We utilize Akaike Information Criterion (AIC) and Bayesian Information Criterion (BIC) as our model selection criteria and we assess model performance via leave-one-out cross-validation. We identify the most influential geographic factors that are associated with two to three categories of similar diurnal trends for each pollutant. With these variables, we will be able to group Seattle monitoring sites and distinguish their diurnal trends. Appropriate adjustment for diurnal trends in our mobile measurements will permit us to estimate spatial contrasts more accurately.