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CO<sub>2</sub>, CH<sub>4</sub> and N<sub>2</sub>O fluxes from soil of a burned grassland in Central Africa

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Table 1. A selection of soil chemical characteristics of the unburned and burned plot soils measured during the first (one month after burning) and second field campaign (eight months after burning) for the top 10 cm of soil
Fig. 1. Soil water filled pore space (%) (0–10 cm soil depth) in function of time after watering (days) during the 1st campaign (A) one month after burning and the 2nd campaign (B) eight months after burning
Fig. 3. Soil respiration normalized at 25 ◦ C, using a Q 10 of 2.78 (g CO 2 m −2 d −1 ) in function of water filled pores space (%) during the 1st campaign (A) one month after burning and the 2nd campaign (B) eight months after burning
Fig. 6. The frequency distribution of single-chambers estimates of N 2 O fluxes (mg N 2 O-N m −2 d −1 ) measured in unburned and burned plots (no water treatment) during the 1st campaign (A) one month after burning (n = 32) and the 2nd campaign (B) eight m
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