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Annex B: Occupancy Taxes in Selected EU Member States
Views sought on the principles of a local discretionary transient visitor levy or tourist tax.
- Part of:
- Transient visitor levy: consultation
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Footnotes
Business and Regulatory Impact Assessment (BRIA) of classifying the Ythan Estuary, Sands of Forvie and Meikle Loch (extension) Special Protection Area.
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4. Project Summary
Annual report of the wildlife observation programme underway at the European Marine Energy Centre (EMEC) in Orkney - Fall of Warness
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Appendix D. Source literature for model parameters.
Report on a project which aimed to develop a model to estimate the population consequences of displacement from proposed offshore wind energy developments for key species of seabirds breeding at SPAs in proximity to proposed Forth/Tay offshore wind
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Annex 1: Campaign responses
Independent analysis of the Talking 'Fracking' consultation.
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2 Introduction
Analysis and summary of an online survey of key stakeholders in the wild capture fishing sector, conducted by Marine Scotland during the COP26 climate change summit in 2021.
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Rationale for Government intervention
Business and Regulatory Impact Assessment (BRIA) of classifying the Ythan Estuary, Sands of Forvie and Meikle Loch (extension) Special Protection Area.
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Highly Protected Marine Areas - policy framework and site selection guidelines: socio-economic impact assessment – methodology
This initial socio-economic impact assessment (SEIA) identifies and assesses potential economic and social effects of HPMAs and proposes a methodology for carrying out the site specific SEIAs.
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Model Fitting: A Case Study Using 0+ Atlantic Salmon
Models of juvenile salmonid abundance are required to inform electrofishing based assessment approaches and potentially as an intermediate step in scaling conservation limits from data rich to data poor catchments. This report describes an approach
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Recommendations for Future Work
Models of juvenile salmonid abundance are required to inform electrofishing based assessment approaches and potentially as an intermediate step in scaling conservation limits from data rich to data poor catchments. This report describes an approach
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