In this study, passive samplers were placed in 10 provinces and an active sampler in Izmir in order to examine the long-range transport of POPs that are released into the environment due to the effects of the war in countries next to our southeast border. The ten cities were classified into three proximity groups: close, middle, and far. According to correlation analysis, central tendency statistics for various congeners showed an increasing trend with proximity to the war zone. However, support by hypothesis testing with Kruskal-Wallis or ANOVA tests were limited: PBDE-183, Σ45PCB and dieldrin in winter, PBDE-28, PBDE-99, PBDE-154, p,p'-DDE, Σ14PBDE and Σ25OCP in the transition period, and PBDE-28, PBDE-99, PBDE-85, PBDE-154, PBDE-190, PCB-52, Σ45PCB, p,p'-DDE and Σ25OCP in the whole sampling period. Back-trajectory frequency analysis of passive sampling indicated that air masses were transported from the war zone to the close region, but it was limited for middle and far regions deeming support by back-trajectory analysis of active sampling not possible, which show that the main route of air masses were Europe, Russia, and the former Soviet Union countries, and North Africa. Concentrations measured by passive air sampling being relatively higher both in the close-group and far-group especially in winter than in the middle-group. The result of passive sampling indicates that the southwest border of Turkey was impacted by POPs which were transported from the war zone while the west of the country was impacted by those from areas in north and northeast.