This work presents the results of a 4-year study on sulfur dioxide (SO₂) ground-level concentrations in an area of southeastern Spain, the L'Alacantí region, where the cement industry is important and coke use extends to other industries as well. The main source of SO₂ emissions in the area was found to be a the Lepold cement plant (one of the two cement plants in the area). The high levels of SO₂ probably extend back to 1920 when this plant began operations. Both local and Mediterranean-scale meteorological processes influence the SO₂ ground-level concentration and together explain the dispersion dynamics of this pollutant. The location and topography of the study zone result in NW Atlantic advections and E-SE sea breezes being the dominant atmospheric circulation patterns in the area. Under stable meteorological conditions, minor local circulations are also relevant to the SO₂ concentration levels. The high frequency of local circulations determines a concentration pattern that changes during the day, with impacts occurring preferentially in a W-NW direction from the source at midday (sea breeze and strong thermal mixture), and in a SE direction at night. This causes the SO₂ concentrations to present well-defined diurnal cycles with well-differentiated shapes depending on the location of the sampling station relative to the source. The dependence of SO₂ 10 min levels on the wind origin and speed throughout the day has been evaluated by studying statistical parameters including P95, P50 and arithmetic mean. Exceedances occur under specific dispersion conditions at distances less than 1 km from the source. However, the source is traceable at larger distances and the levels are higher than typical urban ones. P95 was used as an estimator of the occurrence of larger levels or impacts. Leeward of NW winds and the source, at night and in early morning, P95 levels are comprised between 30 and 55 µg m⁻³. In contrast, with SE winds and at midday, P95 levels stay at 17 µg m⁻³. The same P95 was obtained for winds lower than 5 m s⁻¹, which represent 89% of the winds in the area. However, stronger winds can have P95 levels above 125 µg m⁻³.