Denna policybrief (D4.1) har tagits fram som en del av Horizon Europe PLAN-B-projekt (bidragsavtal nr. 101135308) i samarbete med sitt systerprojekt AquaPLAN (bidragsavtal nr. 101135471). Denna policybrief ger strategisk vägledning för Europeiska unionen att hantera ljusföroreningar, erkänna dess negativa miljöpåverkan, harmonisera insatser och tillhandahålla ett ramverk för samordnade nationella åtgärder, samt att främja vetenskapsbaserad reglering och hantering av artificiellt ljus på natten (Artificial Light at Night, ALAN). För att stödja politiska åtgärder för att minska ljusföroreningar uppmuntras individer att underteckna ett stödformulär, medan organisationer kan stödja initiativet genom att underteckna ett stödbrev, vilket finns tillgängligt på begäran från de kontakter som anges i policybriefingsdokumentet. Rekommenderad citeringYakushina, Y., Klenke, R., Fletcher, D., Jones, L., Nascimento, A. T. A., Teixeira, C. P., Goulart, V. D. L. R, Maggi, E., Hoelker, F., Barnett, C., Tysiac, P., Sanchez de Miguel, A., Sheriff, G., Lomas, M. J., Van Hoorick, G., & Wood, M.D. (2025). Restoring the night: A policy agenda for light pollution mitigation in Europe. Policy brief written by the PLAN-B project (Horizon Europe No. 101135308) and the AquaPLAN project (Horizon Europe No. 101135471). Översatt av Henrik Sandgren. Zenodo. Disclaimer This publication was produced under the Horizon Europe programme (Grant Agreement No. 101135308) as part of the PLAN-B project. The content reflects only the views of the authors. The European Commission is not responsible for any use that may be made of the information contained herein. The information is provided “as is” without warranty of fitness for a particular purpose. The PLAN-B Consortium accepts no liability for any direct, indirect, or consequential damages arising from its use. This is a Swedish translation of the Policy Brief “Restoring the Night: A Policy Agenda for Light Pollution Mitigation in Europe” (published June 2025) (access the original version here).
A coastal grassland was used as a model system to examine how grazing management, un-grazed (for six years), rabbit grazed or fully grazed (ponies 0.2ha−1, cattle 0.05ha−1 and rabbits 45ha−1), affected biodiversity and ecosystem service provision, by measuring an extensive suite of biophysical variables as proxies for ecosystem services. For ‘supporting services’, nutrient cycling was greatest in un-grazed grassland but primary productivity did not differ. The ‘provisioning service’ of food production was only provided by fully grazed grassland. For grazing effects on ‘regulating services’ total carbon (C) stock did not differ and effects on pest regulating invertebrates and pollinator abundance were variable. The potential for flood control was considered greatest in the un-grazed grassland; with faster water infiltration than in the fully grazed grassland. The ‘cultural service’ of environmental appreciation was considered higher in fully grazed grassland due to significantly greater plant species richness, more forb species and more forbs flowering than in un-grazed grassland.
Este resumen de políticas (D4.1) se crea en el marco del proyecto PLAN-B de Horizon Europe (acuerdo de subvención Nº 101135308), en colaboración con su proyecto hermano AquaPLAN (acuerdo de subvención Nº 101135471). Este resumen proporciona directrices estratégicas para que la Unión Europea avance en el abordaje de la contaminación lumínica, reconociendo sus impactos ambientales adversos, coordinando esfuerzos y ofreciendo un marco para la acción nacional conjunta, así como promoviendo la regulación y gestión de la iluminación artificial nocturna (ALAN, del inglés Artificial Light at Night) basada en evidencia científica. Para apoyar las medidas políticas encaminadas a reducir la contaminación lumínica, se alienta a las personas a firmar un formulario de apoyo, mientras que las organizaciones pueden apoyar la iniciativa firmando una carta de apoyo, que está disponible a solicitud a los contactos que figuran en el documento informativo sobre políticas. Cita recomendada Yakushina, Y., Klenke, R., Fletcher, D., Jones, L., Nascimento, A. T. A., Teixeira, C. P., Goulart, V. D. L. R, Maggi, E., Hoelker, F., Barnett, C., Tysiac, P., Sanchez de Miguel, A., Sheriff, G., Lomas, M. J., Van Hoorick, G., & Wood, M.D. (2025). Restoring the night: A policy agenda for light pollution mitigation in Europe. Policy brief written by the PLAN-B project (Horizon Europe No. 101135308) and the AquaPLAN project (Horizon Europe No. 101135471). Traducido al español por Florencia Reichmann & Daniel Lisbona. Zenodo. Disclaimer This publication was produced under the Horizon Europe programme (Grant Agreement No. 101135308) as part of the PLAN-B project. The content reflects only the views of the authors. The European Commission is not responsible for any use that may be made of the information contained herein. The information is provided “as is” without warranty of fitness for a particular purpose. The PLAN-B Consortium accepts no liability for any direct, indirect, or consequential damages arising from its use. This is a Spanish translation of the Policy Brief “Restoring the Night: A Policy Agenda for Light Pollution Mitigation in Europe” (published June 2025) (access the original version here).
Investigations are in progress to determine the potential for ASR, in the Cretaceous Lower Greensand aquifer at Horton Kirby, to meet demand during droughts of up to 2 years, whilst also meeting normal seasonal demands. The sands and sandstones are glauconitic and ferruginous so an understanding of the hydro geochemistry is needed to predict the responses to injection of aerobic water from the overlying Chalk aquifer. Pumped and pore water from the aquifers have been characterised, microcosm experiments undertaken and the results used to constrain geochemical modelling. The transmissivity of the 23 m thick aquifer is calculated to be 45 m2/d and it contains Ca-HCO3 type groundwater with a pH of 7.6 and a SEC of 329 μS/cm. Concentrations of Fe(total) and Mn exceed the prescribed concentration value (PCV). The water to be injected is also a Ca-HCO3 type with a pH of 7.4 and a SEC of 537 μS/cm, is aerobic and contains elevated concentrations of nitrate (22 mg/l), but not in excess of limits. Likely impacts of ASR are reactions with Fe-minerals (including small quantities of pyrite) resulting in an increase in dissolved iron and sulphate, and removal of injected nitrate through reduction.