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, Table 1 -Main characteristics of the three forest sites selected for this study, MAT= Mean, vol.657
, Annual Temperature; MAP= Mean Annual Precipitation (for the study period, 2014.
, Table 2 -Initial leaf litter quality of each litter species: Quercus pubescens, Quercus ilex and 666
, One-way ANOVA was performed to test 667 differences between initial litter species. F-Ratio are indicated and P-values with the 668 respective symbols * for P < 0.05, ** for P < 0.01, and *** for P < 0.001. Different letters 669 denote significant differences among species with a>b>c, Pinus halepensis. Values are mean ± SE (n=5)
, Table 3 -ANOVA table of F-Ratio and P-values for the effects of forest sites (S), litter 674 species (L) and drought conditions (D) on the mass loss, microbial biomass (actinobacteria, 675 bacteria and fungi) and actinobacteria/ fungi (A/F) and bacteria/ fungi (B/F) ratios
, 10 gene 691 copy number g -1 litter dry mass) for each litter species at each forest site and drought 692 condition (ND = Natural drought; AD = amplified drought). One-way ANOVAs were 693 performed for differences among litter species per drought condition and forest site. F-Ratio 694 are indicated and P-values with the respective symbols * for P, p.695
Different letters denote significant differences among litter species with 696 a>b. T-tests was performed to test the effect of drought conditions for each species at each 697 forest site. T-test are indicated and significant P-values ,
, At each forest site
, Supplementary Figure 2 -Rain exclusion devices in the three forest studied (a) Quercus 736 pubescens forest at O 3 HP, (b) Quercus ilex at Puéchabon and (c) Pinus halepensis at Font
, Quercus ilex and Pinus halepensis) coming from natural drought 744 (ND) were redistributed and 2) placed in the three different forests, p.745
, Quercus ilex Puéchabon and Pinus halepensis Font-Blanche forest, respectively), under 746 natural drought (ND) and amplified drought (AD) conditions