There is an increasing concern about the negative impacts associated to the release of reactive nitrogen (N) from highly fertilized agro-ecosystems. Ammonia (NH₃) and nitrous oxide (N₂O) are harmful N pollutants that may contribute both directly and indirectly to global warming. Surface applied manure, urea and ammonium (NH₄⁺) based fertilizers are important anthropogenic sources of these emissions. Nitrification inhibitors (NIs) have been proposed as a useful technological approach to reduce N₂O emission although they can lead to large NH₃ losses due to increasing NH₄⁺ pool in soils. In this context, a field experiment was carried out in a maize field with aiming to simultaneously quantify NH₃ volatilization and N₂O emission, assessing the effect of two NIs 3,4‑dimethilpyrazol phosphate (DMPP) and 3,4‑dimethylpyrazole succinic acid (DMPSA). The first treatment was pig slurry (PS) before seeding (50 kg N ha⁻¹) and calcium ammonium nitrate (CAN) at top-dressing (150 kg N ha⁻¹), and the second was DMPP diluted in PS (PS + DMPP) (50 kg N ha⁻¹) and CAN + DMPSA (150 kg N ha⁻¹) also before seeding and at top-dressing, respectively. Ammonia emissions were quantified by a micrometeorological method during 20 days after fertilization and N₂O emissions were assessed using manual static chambers during all crop period. The treatment with NIs was effective in reducing c. 30% cumulative N₂O losses. However, considering only direct N₂O emissions after second fertilization event, a significant reduction was not observed using CAN+DMPSA, probably because high WFPS of soil, driven by irrigation, favored denitrification. Cumulative NH₃ losses were not significantly affected by NIs. Indeed, NH₃ volatilization accounted 14% and 10% of N applied in PS + DMPP and PS plots, respectively and c. 2% of total N applied in CAN+DMPSA and CAN plots. Since important NH₃ losses still exist even although abating strategies are implemented, structural and political initiatives are needed to face this issue.