BUSCADOR RECOLECTA

Additional file 2: Figure S1. Event-history diagram for each salinity condition. Figure S2. Survival as adults by sex; Kaplan–Meier curves estimated for males and females who reached adult stage in each salinity condition., ’la Caixa’ Foundation MoSquITo project Consejo Superior de Investigaciones Cientificas (CSIC), Peer reviewed

Under a Creative Commons BY 4.0 license., Figure S1. Particle size distribution of Ni-based particles (from CNF growth catalyst) in the rGO-CNF1.0 nanocomposite; Figure S2. Pore size distribution curves obtained by applying BJH method to the desorption branches; Figure S3. XPS signals for Ta 4f for the different TaOx-based catalysts; Figure S4. XRD patterns for the TaOx catalysts supported on rGO-CNF composites as well as rGO and CNF (* line with multiple indexes). The dotted lines (shown only those at Bragg angles above 35º 2theta for the sake of clarity) indicate the position of different reflections and Miller indexes according to ICDD reference patterns (Na2Ta8O21 PDF#28-1137, Ta2O5 PDF#89-2843, TaO PDF#89-4772, Ni PDF#87-0712); Table S1. Lattice parameters from XRD patterns for the tantalum-related phases. The values written in bold correspond to the main component of the tantalum-based formulation., The authors acknowledge Grants PID2020-115848RB-C21 and PID2020-115848RB-C22 funded by MICIU/AEI/10.13039/501100011033, and to the Gobierno de Aragón (DGA) for the funding to Grupo de Investigación Conversión de Combustibles (T06_23R). J.C. Ruiz-Cornejo acknowledges also DGA for his PhD grant., Peer reviewed

Under a Creative Commons BY 4.0 license., Detailed structural information obtained from XRD and Rietveld refinement of the hybrids, UV−vis spectra of all the as-prepared photocatalysts, FESEM images of the control and hybrid photocatalysts, schematic of the g-C3N4 cleavage and impregnation, additional XPS spectra of α-Fe2O3 NPs and α-Fe2O3/g-C3N4 hybrid, additional degradation experiments, and table comparing the photocatalytic activity of different material systems., S1. X-ray diffraction Figure S1. XRD pattern of the (1 0 0) peak of g-C3N4 and hybrid materials. Table S1. Crystallographic parameters of hematite NPs and hybrid materials. S2. UV-vis absorption spectroscopy Figure S2. UV-vis spectra of the reference and hybrid materials. S3. XPS of Fe 2p core spectra Figure S3. Fe 2p XPS spectra of α-Fe2O3 NPs and α-Fe2O3/g-C3N4 hybrid. S4. Cleavage and impregnation of g-C3N4 Figure S4. Schematic of the cleavage and impregnation process of the g-C3N4 sheets. S5. High resolution FESEM Figure S5. High-resolution FESEM micrographs of α-Fe2O3 NPs, g-C3N4 and hybrids. S6. Additional photocatalytic MB degradation results Figure S6. Effect of H2O2 and UV light on MB degradation. Figure S7. Comparison between UV and white ligh on MB degradation. Figure S8. MB degradation using different concentrations of photocatalyst. Figure S9. Comparative degradation of MB, RhB and MR. Figure S10. XRD analysis of the photocatalyst after recycling experiment. Figure S11. UV-vis spectra of time-dependent MB degradation. S7. Comparative table Table S2. Comparison of the photocatalytic activity and degradation time employing different material systems and experimental conditions. S8. References., Funding from Spanish MCIN/AEI/10.13039/501100011033 and “ERDF A way of making Europe” under project grant PID2022-139671OB-I00, as well as from the Gobierno de Aragón (DGA) under projects T03_23R (Grupos de Investigación Reconocidos), is acknowledged. A.G.-G. is thankful for his Margarita Salas Postdoctoral Fellowship grant (RSU.UDC.MS21). R.A. acknowledges funding by the Spanish MICIU (PID2019-104739GB-I00/AEI/10.13039/501100011033, PID2023-151080NB-I00/AEI/10.13039/501100011033, and CEX2023-001286-S MICIU/AEI/10.13039/501100011033) and by DGA under project E13-23R. The work at Argonne National Laboratory (N.J.Z./R.A.) was supported by the Advanced Materials for Energy Water Systems (AMEWS) Center, an Energy Frontier Research Center funded by the U.S. Department of Energy, Office of Science, Basic Energy Sciences at Argonne National Laboratory under contract DE-AC02-06CH11357, as well as in part by the National Science Foundation Major Research Instrumentation (MRI) Program (NSF DMR-2117986) at the University of Chicago. The Argonne Picoprobe AEM was developed under CRADA 1300701 between Argonne National Laboratory and Thermo Fisher Scientific Instruments. S.C. thanks the Fund for scientific research - Flanders (FWO) for infrastructure funding for the EPR equipment (I004920N)., Peer reviewed

Supplementary figures to the main publication., Peer reviewed

Supplementary Figs. 1–3., Peer reviewed

Most luminescence-based technologies to determine the pharmacological properties of G Protein-Coupled Receptors (GPCRs) rely on the overexpression of genetically modified receptors. However, it is essential to develop approaches allowing the specific labelling of native receptors. Here we report an innovative approach based on the use of molecular modules to build fluorescent ligand-directed probes that can label aminergic GPCRs. Such probes are readily prepared with a click reaction between a ligand that may include nucleophilic groups and a fluorescent electrophilic linker. The rapidity of click reaction before receptor labelling prevents a side reaction between the nucleophilic ligand and the electrophile. This approach allowed us to label D1 receptor in transfected cells and native receptors in neural cell lines, leaving the receptor fully functional. This approach will pave the way to develop new reagents and assays with which to monitor endogenous GPCRs' distribution, trafficking, activity or binding properties in their native environment., Peer reviewed

This study investigates the geochemical composition of sands and sandy soils collected from 10 playgrounds and 13 parks across the Barcelona Metropolitan Area (BMA), a region characterised by high population density, extensive industrial activity, and heavy traffic. By examining the variability in metal loads and the deposition of contaminants, the research sheds light on the impact of urban pollution sources on the spatial distribution of harmful elements. The findings reveal that playgrounds tend to exhibit coarser sand textures compared to parks, likely reflecting both the progressive milling of sand and the accumulation of deposited particulate matter (DPM) over time. Several parks exhibited significant enrichment factors (EF) (5 ≤ EF ≤ 20) for a variety of elements, which can be attributed to vehicle wear, while others showed even higher enrichments, particularly related to braking systems. Distinct anomalies in metal concentrations were found in several parks, indicating a diversity of pollution sources, including industrial emissions and port activities. Particularly noteworthy are the elevated Ce/La ratios (1.79–2.95) found in some parks, which point to vehicular catalytic emissions. Additionally, exceptional anomalies in Pb (EF: 62.3–84.1) and Sb (EF: 26.8–44.4) concentrations were identified, most likely due to industrial and port activities near certain parks. Another significant finding of this study is the higher concentrations of traffic-related metals found beneath tree canopies compared to open spaces. This suggests that the presence of vegetation, particularly trees, plays a crucial role in modifying the deposition and distribution of PM in urban green spaces. This research provides critical insights into urban pollution dynamics, particularly the distribution of metals in relation to sand composition, environmental interactions, and the role of urban greenery in mitigating the negative effects of airborne pollutants. By examining both the geochemical impacts of pollution and the physical processes that contribute to contamination in urban environments, this study underscores the importance of thoughtful urban green infrastructure in reducing the environmental and health risks associated with urban pollution., Open Access funding provided thanks to the CRUE-CSIC agreement with Springer Nature. This study receives support from the RI-URBANS project (Research Infrastructures Services Reinforcing Air Quality Monitoring Capacities in European Urban & Industrial Areas), funded by the European Union’s Horizon 2020 research and innovation program, Green Deal, European Commission, under grant agreement No 101036245. The authors express gratitude to the Generalitat de Catalunya (AGAUR 2021 SGR00447) and the Direcció General de Territori for their contributions. Patricia Cordoba extends appreciation to the Ministerio de Ciencias e Innovación y Universidades for the Ramon y Cajal fellowship (RYC2021 - 031153-I) award., Peer reviewed

The full data package associated with the review, including collected study data, risk of bias assessments, analyses, and references (ZIP file)., Postpartum haemorrhage (PPH) is the leading cause of maternal mortality worldwide. Prophylactic uterotonic agents can prevent PPH. The current World Health Organization (WHO) recommendation for preventing PPH is 10 IU (international units) of intramuscular or intravenous oxytocin. Several uterotonics prevent PPH, but there remains uncertainty about the most effective agent with the fewest side effects. This is an update of a review first published in April 2018, and incorporates trustworthiness screening of eligible trials., Peer reviewed

Figure S1. H-NMR of HT-PA. -- Figure S2. C-NMR of HT-PA . -- Figure S3. HRMS of HT-PA. -- Figure S4. Evaluation of the synergistic effect of PA and HT on A549 cells. -- Figure S5. Evaluation of the stability of HT-PA on MRC5 and T. Brucei cell culture medium. --, Peer reviewed

Datos de Intensidad de difracción de rayos X en función del ángulo de Bragg.- Los datos se generaron en la línea MSPD de ALBA.- Es un fichero de texto, que se puede leer con cualquier programa de procesador de texto, además de con los programas de tratamiento de datos de difracción de rayos X, como por ejemplo Fullprof, Match! etc. ., Synchrotron X-ray powder diffraction data of Eu3Ta2ON5 acquired at ALBA (experiment number AV-2024028275) with detailed information on acquisition conditions., With funding from the Spanish government through the ‘Severo Ochoa Centre of Excellence’ accreditation (CEX2023-001263-S)., No