BUSCADOR RECOLECTA

Calibration curves for Seebeck measurements; photograph of the device; ac electrical conductivity measurements for different oxygen atmosphere; and Arrhenius-like plot of the experimental resistivity as a function of temperature., Peer reviewed

Histogram of the holes’ random distribution. Maximum holes’ shift, corresponding disorder level η, and porosity. Schematic illustration of Brillouin light scattering geometry and samples’ design. Calculated phonon dispersion of ordered PnC., Peer reviewed

Materials and Methods: graphene CVD growth and wet transfer, graphene macroelectrodes preparation, PEIS measurements and fitting, Raman spectroscopy and spectroelectrochemistry, AFM/KPFM, numerical simulations. Figure S1: Schematic top view of the electrodes design. Figure S2: Cyclic voltammetry of pyrex/graphene. Figure S3: Pyrex/graphene and ITO/graphene Bode curves with complete data set and fitting. Figure S4: Bare ITO Bode curves with complete data set and fitting. Figure S5: Statistics on CPE modulation with voltage of the pyrex/graphene and ITO/graphene electrodes. Figure S6: Bare ITO UPS measurement and work function calculation. Figure S7: Bare ITO carrier density calculation. Figure S8: Au/graphene and bare Au Bode curves with complete data set and fitting. Figure S9: Raman spectroelectrochemistry on an Au/graphene electrode. Figure S10: Si/SiO2/graphene Bode curves with complete data set and fitting. Figure S11: Raman spectroelectrochemistry on an Si/SiO2/graphene electrode. Figure S12: ωG Raman maps of a pyrex/graphene electrode. Figure S13: KPFM on a graphene device before and after PBS immersion. Figure S14: Equivalent electronic circuit describing electrode areas with water intercalation. Figure S15: Simulation of CITObulk and CITOconf. Figure S16: Charge density profiles of the confined water region and bulk electrolyte as a function of the bias for different values of permittivity of the intercalated water. Figure S17: Contribution of the confined water region and the bulk electrolyte to the total capacitance for different values of permittivity of the intercalated water. Figure S18: Charge density profiles of the confined water region and bulk electrolyte as a function of applied voltage for different thicknesses of the intercalated water. Figure S19: Contribution of the confined water region and the bulk electrolyte to the total capacitance for different thicknesses of the intercalated water., Peer reviewed

[Description of methods used for collection/generation of data] Camara traps., [Relationship between files, if important] Each file is a sequence of photos captured by camera tramps., Peer reviewed

Peer reviewed

TEM image and histograms of bare gold nanorods, UV–vis–NIR spectra of AuNRs–cellulose composites, TGA analysis results, EDS elemental maps, XPS analysis results, effect of pH on the photoregeneration of NADH, UV–vis spectra of the samples during investigations of the mechanism of cellulose-assisted photocatalysis, UV–vis spectra of the photocatalyst after each recycling cycle, and UV–vis spectra of all of the control experiments., Peer reviewed

[Methods] The study was carried out on eight inselbergs (steep-sided granitic rock outcrops) of ca. 1 ha on Mahé, the largest granitic island of the Seychelles archipelago, Indian Ocean (- 4.6953°, 55.4999°, 154 km2, 900 m a.s.l.). To restore inselberg communities, all non-native woody plants were removed from four of the inselbergs between 2011 and 2012 by cutting individual plants and applying herbicide to cut stumps (Kaiser-Bunbury et al., 2015), with follow-up control thereafter. The other four inselbergs remained unchanged with both native and non-native species (Kaiser-Bunbury et al., 2017). To estimate fruit availability at each site, we recorded monthly fruit abundance by counting all ripe fruits of woody fleshy-fruited plant species that are mainly dispersed by endozoochory along fixed linear transects. To collect seed predators, we sampled fleshy fruits monthly at the eight study sites over one year (Sep. 2018 to Aug. 2019). Samples of ten fruits were collected opportunistically from all individuals of fleshy-fruited species with >10 fruits at each site. For further information, please see the "Material and methods" section in the associated manuscript, When non-native species invade ecosystems, coevolved plant-animal interactions and associated ecological functions are altered, often to the detriment of local biodiversity. While mutualistic interactions can benefit from —and assist with— ecological restoration through the removal of non-native species, community-level changes in antagonistic interactions due to restoration are less well understood. Insect seed predators provide important ecosystem functions, but can also have antagonistic effects through pre-dispersal seed predation which can cause fruit abortion or premature fruit drop, potentially affecting plant community composition. Here, we used a network approach and data on trophic interactions from a large-scale field experiment to investigate the differences in insect seed predator communities between native restored sites (where non-native plants were removed) and unrestored sites dominated by non-native plants on the island of Mahé, Seychelles. Restored sites contained more individuals and species of seed predators (up by 81% and 50% respectively), and experienced a greater predation intensity (1.06 ± 0.53 vs. 0.27 ± 0.09), and predator specialisation compared to unrestored sites. The proportion of predated samples was similar between treatments (~14%). Beta diversity, measured as species and interaction turnover, increased at restored sites. Synthesis and applications: Our findings imply that vegetation restoration generates marked biodiversity benefits on native seed predator communities and their interactions. However, removing non-native plants did not result in the elimination of non-native seed predators, which might require targeted control measures. Our results highlight the importance of considering the effects of restoration on antagonistic interactions, in addition to those reported for pollination and seed dispersal services. Management practices should aim to control plant invasions for the conservation of native plant communities that serve as resources and refugia both for mutualists (e.g. seed dispersers, pollinators) and native insect seed-predator antagonists, both of which benefit native ecosystem function., German Research Foundation (DFG): KA 3349/2-2. Portuguese Foundation for Science and Technology: 10.54499/UIDB/04004/2020., Peer reviewed

Experimental details, control experiments, and additional microscopy images, including Figures S1–S22 and Tables S1–S3., Peer reviewed

Additional experimental sections (material characterizations and electrochemical measurements); SEM, TEM, and EDS mappings; BET; contact angle; XRD patterns; Raman spectrum; XPS spectra; UV–vis spectrum; Li2S nucleation; CV; charge and discharge curves; Coulombic efficiency; cycling performance; performance comparison; EIS fitting; sample and computational details in the experiments; and electrochemical properties of porous carbon employed as hosts in LSBs., Peer reviewed

Detailed experimental section and characterization including PXRD diffractograms, 1H NMR spectra, MALDI-ToF data, FESEM images, EDX elemental maps, XPS spectra, 13C CP-MAS solid-state NMR spectrum, N2 isotherm, and UV–vis spectrum., Peer reviewed